[0001] The present invention relates to an electrochemical process for isolating from at
least one water soluble precursor compound comprising a metal or a metalloid element
or two or more thereof having a positive valence, a reaction product of the metal
or metalloid element or two or more thereof, according to the preamble of the first
claim.
[0002] The present invention further relates to a device for carrying out the process of
the invention.
Background of the invention.
[0003] Nano particles and their composites exhibit unconventional electronic, optical, magnetic
and chemical properties with respect to bulk phase particles and macroscopic crystals.
Hence, they offer new or improved properties for application in a wide variety of
fields ranging from catalysis, cosmetics, textiles, nano-electronics, high-tech components
and defense gadgets, to pharmaceuticals, medical uses, sensors and diagnostics. At
the smallest sizes (e.g. < 20-50 nm), nano particle properties typically vary irregularly
and are specific to each size (in
Rao C.N.R., Thomas P.J., Kulkami G.U., Nano crystals: Synthesis, Properties and Applications). Regardless of the method used for their preparation many challenges have to be
to overcome, amongst which controlling particle growth, crystallinity, stability and
reproducibility. A high quality synthesis procedure should desirably produce nano
particles with a narrow size distribution. The narrower the size distribution, the
more attractive the synthesis procedure. The best synthesis procedures available today
produce nano crystals with a size distribution of about 5%. Shape control is also
an important feature. Synthesis methods that provide crystalline nano particles are
preferred, as well as the methods that provide shape stabilization. Particularly preferred
are synthesis methods that do not employ hazardous solvents, thinking of environmental
sustainability.
[0004] Modern methods for synthesizing amorphous or crystalline nano particles may include
chemical reaction steps, as well as physical treatment and biological steps. Chemical
methods for producing crystalline nano particles offer the advantage over physical
methods that milder reaction conditions may be used. In comparison with purely biological
methods, an improved control may be achieved. Chemical methods typically employ the
steps of crystal seeding, permitting particle growth to take place and terminating
particle growth once the desired particle size has been obtained. Since these steps
are often inseparable, synthesis is often initiated by providing a nano crystal precursor,
a solvent and termination (capping) agents. Electrochemical synthesis is often employed
for the production of zero-valent, metal nano crystals, by the steps of oxidative
dissolution of an anode, migration of metal ions to the cathode and reduction to the
zero valent state, nucleation followed by particle growth, addition of capping agents
(typically quaternary ammonium salts containing long-chain alkanes) to inhibit growth,
and precipitation of the nano crystals. The size of nano crystals may be tuned a.o.
by altering current density, varying the distance between the electrodes, controlling
the reaction time, temperature and the polarity of the solvent. Chemical and classical
electrochemical methods typically result in the formation of nano crystals having
an average particle size in the range of 2-100 nm.
[0005] US20060068026 discloses a method for preparing a colloidal stable suspension of naked metal nano
crystals. The method comprises the steps of at least partly immersing into essentially
contaminant-free water, a metallic sacrificial anode that includes an essentially
contaminant-free metal starting material for the nano crystals and a cathode; and
applying a voltage potential across the anode and the cathode to form a colloidally
stable suspension of naked metal nano crystals composed essentially of metal from
the metallic sacrificial anode.
[0006] When analyzing existing methods for synthesizing nano particles, the inventors realized
that the existing techniques can be regarded from a different perspective. The chemical
precursors for the nano particles are usually contained in the solution that is being
treated in a dissolved state, for example dissolved in an aqueous matrix. Formation
of the nano particles and their conversion into a stable solid precipitate, has the
consequence that the water soluble ions are removed from the aqueous matrix. The method
for synthesizing nano particles can therefore also be regarded as a method for removing
water soluble compounds from a solution and recovering them for example as a solid
precipitate.
[0007] This is of special interest in the field of recovery of critical raw mineral materials,
especially those with high technological interest such as the rare earth elements
(REE) which are used in the manufacturing of electronic and telecommunication devices
and high-tech applications, strategic and clean energy technologies and defense instruments
to name a few examples. The REE are ranked as critical raw materials not only due
to their wide applicability, but primarily due to the risk of supply interruption,
but probably also to their economic value. A key measure to anticipate REE supply
vulnerabilities is recycling from end-of-life products; yet this is far from sufficient
to meet the REE demand. As the risk of supply interruption and the value of REE rise,
other matrices not yet prospected start to make economic sense for recovery.
[0008] WO 2012115273 A1 discloses a method for the extraction and separation of lanthanoid elements and actinoid
elements by contacting a solution of these elements with a nanostructure carrying
a metal-adsorbent compound, capable of functioning as an adsorbent for the target
metal. The adsorbent compound with the metal adsorbed to it is contacted with a back-extraction
solution to extract the metal.
[0009] Another method for removing ionic species from fluids, for example impaired water
supplies, which makes use of capacitive deionization is disclosed in
US2011042219. The method disclosed in
US2011042219 employs an electrodialysis and/or an electrodialysis reversal system that utilizes
high-surface area, porous, non-Faraday electrodes. The system contains a membrane
stack which includes alternating cation-transfer membranes and anion-transfer membranes,
as well as a porous cathode and a porous anode. As direct current power is passed
through the electrodes, cations and anions migrate to opposing electrodes, thereby
causing a separation of the saline water into concentrate and dilute stream lines.
A double layer capacitor with a high apparent capacitance may be thus formed on each
electrode. The method is typically applicable in industries in which liquids may require
ionic species removal including water, pharmaceuticals and food and beverage industries.
[0010] However, the above described methods do not provide true, economically feasible recovery
rates, where possible in a form which permits re-use of the metal. The existing extraction
methods for extracting REE or other critical metals from aqueous matrixes, e.g. to
meet regulatory requirements, are insufficient and need to be adapted to provide a
commercially interesting product.
[0011] The present invention therefore also aims at providing an economically feasible method
for isolating from a matrix, in particular an aqueous or water based matrix, at least
one water soluble precursor compound comprising a metal or a metalloid element or
two or more thereof having a positive valence.
[0012] This is achieved by the present invention with a method which shows the technical
features of the characterising portion of the first claim.
[0013] Thereto, in the electrochemical process electrochemical process for isolating from
at least one water soluble precursor compound comprising a metal or a metalloid element
or two or more thereof having a positive valence, a reaction product of the metal
or metalloid element or two or more thereof, the water soluble precursor compound
is supplied to a water based catholyte contained in a cathode compartment of an electrochemical
cell containing a cathode with an electrochemically active surface in contact with
the catholyte. The cathode is subjected to an electric potential, which is chosen
such as to cause reduction of an oxidant gas present at the cathode to one or more
corresponding peroxide, ionic and/or radical species capable of reacting with the
metal or metalloid element, and to cause conversion into a reaction product comprising
a compound which consists of the metal or metalloid element or two or more thereof
on the one hand and the peroxide, ionic and/or radical species on the other hand,
in particular into nano particles of the reaction product.
[0014] The inventors have observed that subjecting the cathode to an electric potential
which is chosen such that it is capable of causing reduction of the oxidant gas, a
redox transformation of the metal and/or metalloid ion present at the electrochemically
active surface of the cathode changes to a higher electrochemical oxidation state.
Thereby the metal and/or metalloid cations dissolved in the catholyte get oxidized
and form an interface with the electrolyte, which adheres at least temporarily to
the electrochemically active surface of the cathode.
[0015] The inventors have observed that the oxidized metal and/or metalloid cations may
accumulate at that interface, in a physical state which is different from the physical
state of the surrounding electrolyte, so that they may be separated therefrom. Depending
on the nature of the metal or metalloid cation, the reaction product may for example
accumulate on the interface in the form of crystalline or amorphous nano particles,
which may grow with time to take a larger size as the reaction proceeds, to form a
different physical state which is different from the physical state of the electrolyte
and permits isolation of the reaction product from the cathode and the electrolyte.
The reaction product may be released in a variety of physical forms, for example in
the form of a precipitate, or in the form of colloidal nano particles, for example
in the form of a colloidal dispersion. After having been released into the electrolyte,
the particles may further aggregate to form a stable solid phase, a separable precipitate
or gel phase.
[0016] Metal and metalloid ions may take various oxidation states and form with the species
which result from the reduction of the oxidant gas, reaction products or compounds
which contain one or more polyatomic ions, in an oxidation state which leads to a
phase that may be separated from the catholyte and from the cathode. The skilled person
will be capable of identifying those oxidized compounds which form a separable phase
in a water based electrolyte, and select the appropriate electric potential and pH.
Pourbaix "Atlas of electrochemical equilibria in aqueous solutions", second edition
1974 discloses the solubility and stability as ions or solid compounds of several
metals and their oxides as a function of the voltage potential and the pH. Diagrams
for a wide variety of species can be constructed based on the premises provided therein.
The skilled person is capable of identifying the electric potential at which electrochemical
reduction of the oxidant gas, and the corresponding oxidation of the metal cation
or metalloid cation may occur. The inventors have further observed that varying of
the electrochemical potential at the cathode, permits to control the chemical composition
of the reaction product.
[0017] Without wanting to be bound by this theory, the inventors assume that the reduction
of the oxidant gas present in the cathode compartment may give rise to the formation
of one or more peroxide, ionic and/or radical species, usually polyatomic species,
which are adsorbed to the electrochemically active cathode surface.
[0018] The inventors further believe that the water soluble precursor compound is dissolved
in the electrolyte, in particular in the catholyte, in an at least partly dissociated
state :
MA ↔ M
+ + A
-
and that the metal ion or the metalloid ion or a mixture of two or more hereof, may
migrate from the solution towards the cathode and adhere to the electrochemically
active surface of the cathode, whereby an electric double layer may be formed. Adhesion
of the metal or metalloid ion may take place through various mechanisms, for example
capacitive adsorption or reversible ion exchange adsorption, complexating or chelation,
but any other forms of adhesion may take place as well.
[0019] The inventors further believe that at least part of the functional groups present
on the surface of the electrochemically active layer will be present in an at least
partially dissociated state (
C*-R-), especially when an electric potential is applied to the electrode. These dissociated
charged sites
C*-R- may form ion exchange sites for the positively charged metal or metalloid ion. The
surface of the electrochemically active layer may for example comprise weak protonic
acid sites in the form (
C*-RH), where C* represents an active site on the electrochemically active layer of the
cathode.
[0020] In the presence of an oxidant gas such as oxygen or any other oxidant gas, the availability
of the active sites in a dissociated state may accelerate:
C*-R- +
O2(g)+
e- →
C*-RO2ad•-
C*-RO2ad•- +
H2O +
e- →
C*-RO2ad•Had +
OH
C*-RO2ad•Had +
e- → C*-R- +
HO2-aq
[0021] A positively charged metal or metalloid ion may be adsorbed either directly to a
C* - R- site or to a reduced species of the oxidant gas, for example a peroxide radical,
an ionic or other radical species, the peroxide radical being the most active situation,
thereby forming a polymetal ion polyoxy radical, which may act as a nucleation site
for the formation of the oxidized compound on the surface of the electrochemically
active material of the cathode. For the case of the cerium ion (Ce
3+), this may lead to the following reactions :
C*-RO2ad•- + 2
Ce3+ +
2e- →
C*-RO2ad2Cead
C*-RO2ad2Cead + 2
O2 (g) + 2e- →
C*-RO2ad2Cead2O2ad•
C*-RO2ad2Cead2O2ad• +
H2O +
H+ +
2e- →
C*-RO2ad2Cead2O2ad2Had+OH-
[0022] It is further believed that the ionic or radical species of the oxidant gas may diffuse
over the charged electrochemically active surface and cluster with other similar species,
for example peroxide radicals, adhering to the active surface of the cathode.

This may lead to local super-saturation and the growth of the surface peroxide into
critical nuclei.
[0023] The inventors assume that the electrochemical process of this invention is capable
of catalyzing an in situ oxidation of a metal or metalloid ion dissolved in the aqueous
electrolyte to a higher oxidation state, whereas at the cathode typically a reduction
reaction would be expected. This assumption is supported by the observation that the
conductivity of the electrolyte decreases with an increasing degree of separation
of metal or metalloid ion from the aqueous solution.
[0024] Since adhesion forces with which the oxidized compound adheres to the electrochemically
active surface may vary with the nature of the electrochemically active surface of
the cathode and the nature of the oxidized compound, release of the oxidized compound
particles into the electrolyte may occur as such or may need to be forced.
[0025] Preferably, the electric potential to which the cathode is subjected, is a reducing
potential relative to a reference electrode, preferably below the thermodynamic pH-potential
equilibrium region of stability of the oxidant gas in water, more preferably below
the region of thermodynamic stability of water but preferably not within the region
of thermodynamic stability of hydrogen. This way the risk to the occurrence of water
electrolysis to form hydrogen may be minimized.
[0026] Although the electrochemically active surface of the cathode may contain adsorbed
reactive radicals and/or adsorbed oxidant gas, and although the water based electrolyte
may contain some dissolved oxidant gas, this will usually not be enough to ensure
full recovery of all metal or metalloid ions dissolved in the electrolyte. Supply
of an oxidant gas to the cathode may therefore be preferred in order to ensure maximum
recovery of the metal ions dissolved in the water based electrolyte and optimize the
reaction rate. Preferably, the oxidant gas is supplied through a hydrophobic gas-diffusion
layer of a gas diffusion electrode towards the electrochemically active material.
[0027] Examples of oxidant gases suitable for use with this invention include organic as
well as inorganic oxidant gases. Example of inorganic gases suitable for use with
this invention include ozone, oxygen, carbon oxide gases for example CO
2, nitrogen oxides for example NO, N
2O
3, halogen gases,halogen oxide gases, sulfur oxide gases, air, biogas, flue gas, acid
gas and combustion exhaust gas and mixtures or two or more of the afore mentioned
gases. Preferably however, use is made of air. Other oxidant gases suitable for use
with this invention include those capable of forming oxidant mono-atomic radicals
and/or oxidant polyatomic radicals.
[0028] Particularly preferred oxidant gases are those which may be reduced so as to generate
polyatomic ions, polyatomic radicals or polyatomic peroxides, for example those are
summarized in the table below:
| perchlorate |
ClO4-1 |
hydrogen sulfate |
HSO4-1 |
hydrogen phosphate |
HPO4-2 |
| chlorate |
ClO3-1 |
dihydrogen phosphate |
H2PO4-1 |
peroxide |
O2-2 |
| chlorite |
ClO2-1 |
permanganate |
MnO4-1 |
tetraborate |
B4O7-2 |
| hypochlorite |
ClO-1 |
periodate |
IO4-1 |
borate |
BO3-3 |
| nitrate |
NO3-1 |
hydrogen carbonate |
HCO3-1 |
|
|
| nitrite |
NO2-1 |
sulfate |
SO4-2 |
|
|
| bromate |
BrO3-1 |
sulfite |
SO3-2 |
|
|
| iodate |
IO3-1 |
carbonate |
CO3-2 |
|
|
[0029] The oxidant gas is preferably selected such that one or more of the preferred polyatomic
ions is generated, in particular one or more of the polyatomic ions selected from
the group of acetate (CH
3COO
-), acetylide (C
22-), carbonate (CO
32-), peroxide (O
22-), phosphate (PO
43-), sulfate (SO
42-), nitrate (NO
3-).
[0030] According to another preferred embodiment, the at least one oxidant gas is selected
from the group of organic gases, including ethers (e.g. ethylene oxide, propylene
oxide), alkenes (e.g. ethylene, propylene), alkynes (e.g. acetylene), or conjugated
dienes (e.g. butadiene) or mixtures of two or more of these gases.
[0031] The oxidant gas may be used as such or in a mixture with one or more inert gases,
for example N
2, Ar or He or a mixture of two or more of these gases.
[0032] The partial pressure of the oxidant gas within the gas mixture is not critical to
the invention and may vary within wide ranges. Varying the oxidant gas partial pressure
will permit to control the size of the metal or metalloid particles isolated from
the composition containing the precursor compound. Varying the oxidant gas partial
pressure, in particular increasing or decreasing the partial pressure, will also permit
to control, in particular to increase or reduce the lattice parameter of the crystalline
particles of the reaction product, as measured by X-ray diffraction measured over
a given crystallographic plane or transmission electron microscopy imaging.
[0033] The nature of the compound which may be isolated from the solution may be varied
by selecting the appropriate oxidant gas. When O
2 or an O
2 containing gas is supplied as the oxidant gas, the compound will usually take the
form of an oxide or a mixed oxide of the metal or metalloid ion. When CO
2 or a nitrogen oxide gas is supplied as the oxidant gas, the compound may take the
form of a carbonate, a nitrite or a nitrate. In other words, the nature of the anion
of the reaction product may be varied by a proper selection of the oxidant gas.
[0034] The skilled person will be capable of adapting the amount of oxidant gas supplied
and the gas flow rate, to the concentration of water soluble precursor compound that
needs to be isolated from the electrolyte. In particular, it may be desirable to vary
the gas supply rate, in particular in case the process is operated in a continuous
mode where a continuous supply of water soluble precursor compound to be removed takes
place. Moreover, gas supply may create convective mass transfer in the catholyte and
not only promote diffusion of the metal and/or metalloid ions from the water soluble
precursor compound to the electrochemically active surface, but may also facilitate
surface diffusion of reduction products of the oxidant gas, i.e. peroxide ionic and/or
radical species, as well as surface diffusion of adhered metal and/or metalloid ions,
or any intermediate reaction products, and thereby increase the reaction rate. Other
suitable ways to create convective mass transfer comprise those known to the skilled
person, for example the use of a stirrer, gas supply, the presence of a spacer material
capable of creating turbulent flow conditions.
[0035] In a preferred embodiment, the electrochemically active surface of the cathode comprises
a plurality of active sites provided by surface functional groups, wherein the functional
groups preferably contain one or more moieties selected from the group of a nitrogen
containing moiety, an oxygen containing moiety, a chlorine containing moiety or a
sulfur containing moiety..
[0036] To ensure maximum recovery, in a preferred embodiment, before supplying the cationic
water soluble compound, the pH of the electrolyte is adjusted to a pH ≤ 7.0, preferably
a pH in acidic conditions, in which the formation of a solid reaction product would
not be expected by the skilled person. More preferably, before supplying the water
soluble precursor compound, the pH of the electrolyte is adjusted to a pH which is
below the dissociation constant of the acid or salt of the a cationic water soluble
compound, more preferably below 5.0. The inventors have observed the pH of the catholyte
gradually progresses towards alkalinity that in the course of the reaction, often
above the dissociation constant of the acid or salt of the ionic metal or metalloid
compound. In particular the final pH of the catholyte may raise to a value of above
4, often above 6 or 7, more preferably above 9, most preferably above 11.
[0037] In a preferred embodiment of the method of this invention, an amount of a weak protonic
electrolyte is supplied to the catholyte. The inventors have found that the metal
oxidation rate may thereby be accelerated. Without wanting to be bound to this theory,
the inventors believe that the weak protonic electrolyte acts as a catalyst or co-catalyst
in the formation of reactive peroxide, ionic and/or radical species from the oxidant
gas at the cathode and in the electrochemical reactions in which the water soluble
compound is converted into a reaction product that may be separated from the cathode
and the catholyte. The co-catalyst has been found capable of accelerating the oxidation
of the metal cation or metalloid ion towards the separable compound, by accelerating
the availability of reactive species. The inventors have further found that addition
of the weak protonic electrolyte may not only increase the conductivity of the catholyte,
but that it may also increase the current density over the cathode.
[0038] Moreover, the presence of the weak protonic electrolyte has the effect that variations
in the pH of the catholyte in the course of the oxidation reaction, may be reduced
to a minimum. This contributes to minimizing the risk to the occurrence of unwanted
side reactions which would lead to the formation of compounds which could not easily
be separated from the cathode and/or the catholyte and for example be water soluble.
This separability provides an important advantage, as such a process may be suitable
for use in or for direct coupling to isolate reaction products from processes employing
biological material.
[0039] The amount of weak protonic electrolyte may vary within wide ranges but is preferably
not less than a 10 mM solution and preferably not more than a 1.5 M solution, more
preferably the concentration of the weak electrolyte varies between 10 and 500 mM,
most preferably around 100 mM.
[0040] The weak protonic electrolyte may either be a weak protonic acid or a weak protonic
base, depending on the pH range at which the separable compound may be formed. In
particular, the weak protonic electrolyte may be a weak polyprotonic acid or a weak
polyprotonic base.
[0041] A weak protonic acid is a protonic acid which only partially dissociates in water
:
HA
(aq) ↔ H
+(aq) + A
-(aq)
[0042] A weak polyprotonic acid is a weak acid which has more than one ionisable proton
per molecule. The dissociation constant of a weak monoprotonic acid may be represented
by the formula below :

[0043] Preferred weak protonic acids have a pKa of between 2.0 and 8.0, preferably between
3.0 and 7.0, more preferably about 7.0. Examples of weak protonic acids suitable for
use with the present invention include those selected from the group of weak organic
and weak inorganic acids, in particular acetic acid, citric acid, oxalic acid, lactic
acid, gluconic acid, ascorbic acid, formic acid, glycolic acid, potassium monohydrogen
phosphate, potassium dihydrogen phosphate, ammonium chloride, boric acid, sodium hydrogen
sulphate, sodium hydrogen carbonate, ammonium chloride, and mixtures of two or more
hereof. Particularly preferred weak protonic acids are those having a pKa which is
at least one unit higher than the pH of the catholyte.
[0044] Preferred weak protonic bases haves a pKa of between 6.0 and 12.0, preferably between
7.0 and 11.0. Examples of weak protonic bases suitable for use with this invention
include those selected from the group of ammonia, trimethylammonia, ammoniumhydroxide,
pyridine, the conjugated bases of acetic acid, citric acid, oxalic acid, lactic acid,
gluconic acid, ascorbic acid, formic acid, glycolic acid, potassium monohydrogen phosphate,
potassium dihydrogen phosphate, ammonium chloride, boric acid, sodium hydrogen sulphate,
sodium hydrogen carbonate, or a mixture of two or more of the afore mentioned compounds.
[0045] To ensure maximum recovery as solid material, in a preferred embodiment the pH of
the electrolyte is adjusted to acidic conditions, in which the formation of a solid
phase is initially not anticipated. Later, the pH progressively turns more basic as
the reaction progresses, wherein colloidal particles in suspension may become apparent.
[0046] In another preferred embodiment, an ionic water soluble salt is supplied to the catholyte,
with the purpose of controlling, in particular of increasing the ionic strength of
the catholyte. Salts of chloride with an alkali metal ion are preferred, NaCl being
particularly preferred. However other electrolytes may be used as well. An amount
of NaCl higher than 1 g.L-1 is preferred, more preferably the amount added will be
higher than 10 g.L
-1, most preferably at least 30 g.L
-1.
[0047] The process of the present invention shows the advantage that the overall conductivity
of the electrolyte in the cathode compartment, will vary to a minimum extent only
in the course of the process. In particular, virtually no or only a minor decrease
of the overall conductivity has been observed. This is probably due to adhesion of
cations to the electrochemically active surface of the cathode, which will in general
attain a quasi stable level when all of the positive valenced elements to be isolated
have been oxidized and transformed into a separable phase, especially in a batch-wise
operated process. Nevertheless, any unwanted variations in the conductivity may be
compensated by supplying additional electrolyte, or by incorporating into the catholyte
a binary electrolyte. This may be of particular importance when the process of this
invention is operated in a continuous manner, and continuous supply of metal and/or
metalloid ions to be recovered takes place. By the presence of the binary electrolyte,
the electrolytic conductivity may be increased to at least 5 mS.cm
-1, more preferably between 20 and 80 mS.cm
-1 and even more preferably between 20 and 50 mS.cm
-1, and thereby the risk to a varying conductivity as a result of the removal of metal
and/or metalloid ions may be minimised.
[0048] In order to facilitate release of the particles from the cathode and facilitate recovering
of the precipitate, the cathode may be subjected to polarization reversal. Polarisation
reversal may also be used to clean the cathode from any unwanted remainders adhering
thereto. This will permit to recover from the solution at least 10% of the amount
of metal or metalloid ion that had been supplied to the cathode, more preferably to
recover at least 40% thereof and even more preferably to recover at least 80% thereof.
[0049] The electrochemical process of the present invention as described in the present
application makes it possible to remove metal or metalloid ions or any other elements
with a positive valence contained in the precursor compound, in a concentration which
corresponds to at least 20 wt. % of the initial concentration of the element with
a positive valence present in the precursor compound, preferably at least 50 wt. %,
more preferably at least 80% and most preferably more than 90 wt. % of even more than
99% thereof.
[0050] The electrochemical process of the present invention is suitable for isolating a
wide variety of precursor water soluble compounds from the water based electrolyte,
in a wide variety of concentrations. The concentration of the water soluble precursor
may be varied to vary the size of the particles formed on the electrochemically active
surface. The inventors have observed that the crystal size of the nano particles may
increase with increasing precursor concentration, or that the crystal size may decrease
with decreasing precursor concentration.
[0051] The present invention is suitable for isolating a wide variety of compounds from
an aqueous solution of the corresponding water soluble precursor compound. The precursor
compound may for example be a compound of an ion of an element selected from the group
of group II, III and IV elements of the periodic table of elements, C and Si excluded,
the majority of the transition metal elements, the actinides and the lanthanides.
The water soluble compound may also be a compound of an ion of an element selected
from the group of group I elements when in a compound also containing P or S. The
water soluble compound may also be a metal organic compound or complex, or an organic
compound.
[0052] In a preferred embodiment, the at least one precursor water soluble metal compound
is selected from the group of precursor compounds containing one ore more alkali metal
ions, preferably one or more of Li, Na, K, Cs ions, more preferably Li and/or Na.
In a second preferred embodiment, the at least one precursor water soluble ionic metal
compound contains at least one metal ion selected from the group of alkaline earth
metals, in particular preferably Ca and/or Mg. In a third preferred embodiment, the
at metal ion contained in the least one precursor water soluble ionic metal compound
is selected from the group of transition metals, preferably one ore more of Sc, Ti,
V, Cr, Mn, Fe, Co, Ni, Cu, Zn, Y, Zr, Nb, Mo, Pd, Ag, Cd, Hf, Ta, Tu, Re, Ir, Pt,
or Au ions, more preferably one or more of V, Mn, Co, Nb, Ag, Pt or Au ions. In a
fourth preferred embodiment, the at least one metal ion is selected from the group
of post-transition metals, in particular one or more of Al, Ga, In, Sn, Tl, Bi ions.
In a fifth preferred embodiment, the at least one precursor water soluble ionic metalloid
compound is selected from the group of B, Si, Ge, As, Sb, Te, Se or C ions or mixtures
of two or more hereof. In a sixth preferred embodiment, the at least one precursor
water soluble ionic metalloid compound is selected from the group of Li, Na, Ca, Fe,
Mg, Al or Zr ions. In a particularly preferred embodiment, the metal and/or metalloid
ion is selected from the group of wherein the monoatomic cation is selected from the
group of H
+, Li
+, Na
+, K
+, Cs
+, Mg
2+, Ca
2+, Sr
2+, Ba
2+, Al
3+, Ag
+, Zn
2+, Fe
2+, Fe
3+, Cu
2+, Cu
+ and mixtures of two or more hereof.
[0053] The water soluble precursor compound may be supplied as a precursor compound comprising
one single type of metal or metalloid ion or element with a positive valence, but
it is within the scope of this invention that a composition comprising a mixture of
two or more metal ions or metalloid ions or elements with a positive valence may be
supplied as well. In case a single metal or metalloid ion is supplied, the reaction
product that may be separated from the aqueous precursor solution is preferably a
compound comprising one single metal or metalloid in an oxidized state. In case the
electrolyte comprises a mixture of two or more metal or metalloid ions or elements
with a positive valence, the reaction product may comprise a mixture of compounds
of the in an oxidized state, all reaction products for example responding to the formula
MxOy, but it may also comprise mixed metal or metalloid compounds for example MxNzOy.
It is however also within the scope of this invention that a matrix comprising one
a precursor compounds is supplied or a matrix containing a mixture of two or more
precursor compounds.
[0054] In a first embodiment of this invention, the reaction product that is formed from
the precursor compound may contain crystalline oxide nano particles, for example,
but not limited to CeO
2, La
2O
3, Co
2O
3, Al
2O
3, Cs
2O, Li
2O, CoFe
2O
4, FeAsO
4, or non-stoichiometric forms thereof or hydrated forms thereof. In a second embodiment,
the reaction product may contain crystalline carbonate nano particles, preferably
but not limited to Na
3La
3(CO
3)
5, NaHCO
3, or non-stoichiometric forms thereof or hydrated forms thereof. In a third embodiment
of this invention, the separable compound may contains a mixture of amorphous or crystalline
metal oxide nano particles or mixed oxides.
[0055] The particles may be released in a variety of physical forms, for example in the
form of colloidal nano particles, for example in the form of a colloidal dispersion,
a separable precipitate of particles or a gel phase. Usually a stable dispersion or
gel will be obtained. In order to improve the stability, the a dispersion or suspension
of the particles may be subjected to sonication or ultrasonication. According to another
variant, one or more additives may added to the precursor, the suspension or dispersion,
selected from the group of dispersants, stabilizers, surfactants, polymers, copolymers,
emulsifiers, cross-linking agents, capping agents and free flow agents or mixtures
thereof.
[0056] In a preferred embodiment of this invention, the electrochemically active surface
of the cathode preferably comprises a plurality of active sites having a weak protonic
acid functionality, i.e. active sites which only partially dissociate in water. Various
electrochemically active materials may be used to achieve this. Preferred are those
materials which have a surface comprising protonic acid functional groups. Particularly
preferred are those materials which comprise electrically conductive particles of
carbonaceous origin, more preferably those comprising electrically conductive particles
of carbonaceous origin with a catalytically active surface comprising a plurality
of protonic acid groups. It is believed that the protonic acidic functional groups
present on the catalytically active surface, in particular acidic functional groups
of the type R-H, may partly dissociate at a corresponding pH. The inventors also believe
that the thus dissociated surface groups C-R*
- have a high oxygen affinity and thus intervene in the oxidation of the metal ion
or the metalloid ion.
[0057] As electrochemically active material, a wide variety of conductive materials may
be used, but preferred are porous materials, in particular those which contain weak
protonic acid functional groups. Examples of such materials are well known to the
skilled person and include porous metals and metalloids, for example porous nickel
or copper, porous carbon based materials, porous ion exchange resins, carbon aerogels,
silicon, conductive polymers, conductive foams or conductive gels, among others. The
use of a porous carbon based material as or in the electrochemically active surface
is preferred, because of its catalytic activity in combination with a reasonable cost
and abundant availability in comparison to other materials. Examples of suitable materials
include graphite, carbon nanotubes, graphene, carbon black, acetylene black, activated
carbon or synthetic carbons such as vulcan. Other electrochemically active materials
suitable for use with this invention include carbonaceous materials the surface of
which has been chemically modified to adapt its catalytic activity and compatibility
with the reaction medium. Without wanting to be bound by this theory, it is believed
that the presence of oxygen-containing functional groups support the oxidation reaction.
Particularly preferred carbon materials have a surface with quinone-type functional
groups.
[0058] Suitable porous material for use as the electrochemically active layer preferably
have a high specific surface area as measured by the BET method described in ASTM
D5665, in particular a BET surface area of at least 50 m
2/g, preferably at least 100 m
2/g, more preferably at least 200 or 250 m
2/g, most preferably at least 400 or 500 m
2/g, but those having a surface area larger than 750 or 1000 m
2/g or even more may be particularly preferred. Porous materials particularly suitable
for use as the electrochemically active layer include particles of carbonaceous origin,
also those having a small BET surface area, but preferred are those with a high specific
surface area as measured by the BET method, in particular carbonaceous particles selected
from the group of graphite, carbon nanotubes, graphene, carbon black, activated carbon
or synthetic carbons. Preferred conductive carbonaceous particles have a BET surface
area of at least 50 m
2/g, preferably at least 100 m
2/g, more preferably at least 200 or 250 m
2/g, most preferably at least 400 or 500 m
2/g, but those having a surface area larger than 750 or 1000 m
2/g or even more may be particularly preferred.
[0059] The activated carbon preferably has a particle size in the range of 75 to 300 microns,
preferably from 100 to 250 microns.
[0060] Suitable porous material for use as the electrochemically active layer preferably
form a continuous layer on the cathode. Thereto, use can be made of a polymer material
which functions as a support for the electrochemically active material.
[0061] According to another preferred embodiment, the electrochemically active porous material
is a solid which is dispersable or flowable in the water based electrolyte. Hereby,
the solid may be made of one or more of the above described materials.
[0062] In the method of the present invention, preferably use is made of a cathode comprising
a porous gas diffusion electrode, wherein one side of the gas diffusion electrode
comprises a layer of at least one electrochemically active material active for or
capable of catalyzing the reduction of oxygen to hydrogen peroxide. Preferred active
materials have been described above. In order to increase the reaction rate, convective
mass transfer may also be created at least in the cathodic gas compartment.
[0063] A device suitable for carrying out the process of the present invention is shown
in fig. 11. The device shown in fig. 1 comprises an electrochemical cell, comprising
at least one anodic compartment 5 and at least one cathode compartment 15. If so desired
a plurality of anodic and cathode compartments may be present as well. If a plurality
of anode and cathode compartments is provided, they are preferably arranged in a unipolar
arrangement, with a plurality of alternating positive and negative electrodes forming
a stack separated by ion permeable membranes. In a unipolar design, electrochemical
cells forming the stack are externally connected, the cathodes are electrically connected
in parallel as well as the anodes.
[0064] The anode or anodes 1 are immersed in an anode compartment comprising an aqueous
anolyte fluid 2. The cathode or cathodes 10 are immersed in a cathode compartment
comprising an aqueous catholyte fluid 12. The anodic compartment and cathodic compartment
are in fluid communication to allow transport of cations, in particular transport
of protons from the anodic compartment to the catholyte compartment, and transport
of anions from the cathodic compartment to the anodic compartment. As anolyte fluid,
any anolyte considered suitable by the skilled person may be used. In particular any
aqueous electrolyte, conventionally used in electrochemical reduction reactions may
be used. The anolyte may for example comprise an aqueous solution of an electrolyte
selected from the group of sulphates, phosphates, chlorides and mixtures of two or
more of these compounds. The anolyte chamber may comprise a supply member for feeding
anolyte fluid. The catholyte chamber may comprise a supply member for feeding catholyte
fluid. The catholyte may be different from the anolyte, but anolyte and catholyte
may also be the same. Suitable catholyte materials include those well known to the
skilled person, such as an aqueous solution of an electrolyte selected from the group
of sulphates, phosphates, chlorides and mixtures of two or more of these compounds
[0065] The anode and cathode compartment 5, 15 may be made of any material considered suitable
by the skilled person, but are preferably made of a polymeric material. Suitable materials
include polyvinylidene difluoride (PVDF), polytetrafluorethylene (PTFE), ethylene
tetrafluoroethylene (EFTE), polyvinylchloride (PVC), chlorinated polyvinyl chloride
(CPVC), polyacrylate, polymethylmethacrylate (PMMA), polypropylene (PP), high density
polytethylene, polycarbonate and blends or composites of two or more of these compounds.
[0066] The at least one anode and the at least one cathode compartment 5, 15 are preferably
separated from each other by an ion permeable membrane 11 to control exchange of cations
and anions between both compartments. Preferred ion permeable membranes comprise synthetic
polymer materials. The ion permeable membrane on the one hand ensures that cations,
in particular protons, may migrate from the anode to the cathode compartment, and
on the other hand serves as a gas barrier and therewith counteracts the occurrence
of so-called chemical short cuts. The ion permeable membrane also counteracts the
occurrence of a pH reduction of the catholyte in the cathodic compartment. Suitable
materials for use as ion permeable membrane include polyvinyldifluoride (PVDF), polytetra-fluoroethylene
(PTFE or Teflon), poly(ethene-co-tetrafluoroethene (EFTE), polyesters, aromatic polyamides,
polyhenylenesulfide, polyolefin resins, polysulphone resins, perfltiolorovinyl ether
(PFVE), tripropylene glycol, poly-1,3-butanediol or blends of two or more of these
compounds, or composites containing one or more of these compounds and being obtained
by dispersion of a metal oxide and/or a metal hydroxide in a solution of the polymer
to increase the ionic conductivity. The ion permeable membrane may also comprise an
ion exchange material if so desired.
[0067] To improve structural integrity, the ion-permeable membrane 11 separating the anode
and cathode compartment 5, 15 may be reinforced with a rigid support, for example
a rigid support made of a sheet, a fleece, which may be woven or non-woven or otherwise
made of a porous polymer or a web or a mesh of metal fibres or metal fibres arranged
in a woven or non-woven structure.
[0068] The cathode 10 used in the device of this invention is preferably a gas diffusion
electrode, to ensure a sufficiently high mass transfer of oxidant gas to the electrochemically
active surface present at the cathode, and a sufficiently high reaction yield, taking
into account the limited solubility of oxygen in water. The gas diffusion electrode
is preferably a multilayered electrode comprising a current density distributor 3
for supplying electric current to an electrochemically active surface 4 deposited
on top of the current distributor.
[0069] The electrochemically active material 4 is preferably a material which has a higher
electric conductivity than the current density distributor. This permits the electrochemically
active material to take away or bring the electron from and to the current density
distributor.
[0070] The electrochemically active surface may be formed of any conductive materials or
composites with a high surface area. Examples of such electrode materials include
carbon, carbon nanotubes, graphite, carbon fiber, carbon cloth, carbon aerogel, metallic
powders, for example nickel, metal oxides, for example ruthenium oxide, conductive
polymers, and any mixtures of any of the above. It should be appreciated that the
entire electrodes may be porous and conductive enough so that a substrate is not needed.
It should also be appreciated that the substrate may be formed of a non-conductive
material that is coated with a conductive coating, such as, for example, platinum,
rhodium (Rh), iridium (Ir), or alloys of any of the above metals. The high surface
area enables the voltage to be minimized. By contacting the porous portion with the
ionic electrolyte, the apparent capacitance of the electrodes can be very high when
charged.
[0071] The gas diffusion electrode that is used as the cathode 10 in the device of this
invention preferably comprises a current density distributor 3, which may be made
of any material and form considered suitable by the skilled person. Preferably however,
use is made of a mesh type current density distributor, having a mesh received in
a circumferential electrically conductive frame or an array of several meshes. The
current density distributor is connected to a source of electric energy along a current
feeder, for supplying electrical energy to the current density distributor. The mesh
comprises a plurality of electrically conductive paths. The mesh may be formed of
any suitable metallic structure, such as, for example, a plate, a mesh, a foil, or
a sheet having a plurality of perforations or holes. Furthermore, the mesh may be
formed of suitable conductive materials, such as, for example, stainless steel, graphite,
titanium, platinum, iridium, rhodium, or conductive plastic. In addition, the metals
may be uncoated or coated. One such example is a platinum coated stainless steel mesh.
In one embodiment, the mesh is a titanium mesh. In other embodiments, use is made
of a stainless steel mesh, a graphite plate, or a titanium plate. The wording "mesh"
is meant to include a square meshes with a substantially rectangular shape and orientation
of the conductive wires and insulating threads, but the mesh may also be tubular,
or a coil film, or a otherwise shaped three-dimensional materials. Still other types
of meshes suitable for use with this invention include perforated sheets, plates or
foils made of a non-conductive material, having a plurality of wires or threads of
a conductive material interlaced in the direction parallel to the current flow. A
further type of mesh suitable for use with the present invention includes lines/wires
of a conductive material, which extend parallel to the current flow direction, printed
on a perforated sheet, foil or plate.
[0072] One side of the current density distributor 3 may be coated with an electrochemically
active surface 4 capable of catalyzing the reduction of the oxidant gas. The layer
of electrochemically active material 4, i.e. the layer which is catalytically active
in the reduction of the oxidant gas as described above, is preferably applied to the
side of the current density distributor facing the gas phase. The electrochemically
active surface usually has an interface with the electrolyte on one surface (i.e.
the side facing the current distributor) and a water repellant (hydrophobic gas diffusion)
layer 13 on the other side.
[0073] The device preferably comprises a supply member for supplying an oxidant gas to the
side of the cathode comprising the electrochemically active layer.
[0074] The cathode compartment may comprise, preferably on a side opposite the side of the
cathode comprising the electrochemically active layer, an inlet for supplying at least
one weak protonic electrolyte, preferably an aqueous electrolyte. Preferably the flow
rate with which the weak protonic electrolyte is variable.
[0075] The electrochemically active surface 4 may be coated on the side facing the gas phase
13, with a water repellant layer 13 or a hydrophobic gas diffusion layer to minimize
the risk of water leaking through the electrode into the gas phase. This hydrophobic
layer or water repellant layer 13 may also be deposited on top of the electrochemically
active surface 4. Suitable materials for use as the water repellant layer include
polyvinyldifluoride (PVDF), polytetrafluoroethylene (PTFE or Teflon), PSU, but other
materials considered suitable by the skilled person may be used as well.
[0076] The anode 1 used in the device of this invention may be a conventional electrode,
or may be a gas diffusion electrode similar to the cathode. The pH of the anolyte
is preferably acidic, preferably below 5, more preferably below 3.
[0077] The invention is further illustrated in the examples below.
EXAMPLE 1
Materials and Methods
Chemicals
[0078] Activated carbon employed was Norit
® SX1G from Norit Americas Inc. Fluorinated ethylene propylene resin (Teflon® FEP 8000)
was obtained from Dupont. Crystalline ultradry CeCl
3 99.9% (REO) ampouled under argon was received from Alfa Aesar. K
2HPO
4 was procured from Merck. HCl at 35%, CeN
3O
9·6H
2O 99.99% trace metal basis, and analytical grade KI were purchased from Aldrich. 50%
NaOH, analytical grade potassium hydrogen phthalate (KHP), and analytical grade (NH
4)
6Mo
7O
24·4H
2O were acquired from Merck.
Electrochemical cell setup
[0079] Experiments were performed in a half-cell electrochemical reactor (Figure 1). The
cathode half-cell consisted of a cathode, a reference electrode and a counter-electrode.
Ag/AgCl 3 M KCl (+200 mV vs SHE) was used as a reference electrode (Koslow Scientific),
whereas a Pt disk fixed by laser welding over a titanium (Ti) plate was used as a
counter-electrode. All potentials here reported stay true for the Ag/AgCl 3 M KCl
reference electrode. Cathode and counter electrode were separated by liquid electrolyte
and the separating membrane, Zirfon
® (AGFA). Working and counter-electrode were separated from each other by a distance
of 4 cm, whereas the membrane was accommodated right in the middle (at 2 cm from each
electrode). The principal function of Zirfon
® was to prevent oxygen eventually evolved at the counter-electrode from reaching the
working-electrode. The electrodes and separator had a projected electrode surface
area of 10 cm
2. Inert or reactant gas flows (N
2 or air, respectively) were fed through the cathode gas compartment on each individual
experiment. Gas flow rate was set at 400 mL min
-1 (excess) in all cases and an overpressure of 10 mbar was applied. Electrolyte feeds
were independently circulated through the cathode and counter-electrode compartments
with a dual-head peristaltic pump, at a flow rate of approximately 100 mL min
-1 (Watson-Marlow). Both liquid and gas streams under these conditions were consistent
with a laminar flow profile.
[0080] A schematic representation of the experimental electrochemical half-cell reactor
is shown in Figure 1.
Gas diffusion electrodes
[0081] A multilayered VITO CORE™ electrode was used which consists of a current collector
(metal gauze), an active layer made of activated carbon embedded in a porous polymer
matrix, and a hydrophobic gas-diffusion layer. PVDF was used as polymer binder, both
for the active layer and the hydrophobic gas-diffusion layer (GDL). The hydrophobic
particles in the hydrophobic backing were FEP 8000. A typical GDL is composed of 50
wt% PVDF and 50 wt% FEP 8000. The composition of the active layer for the uncatalyzed
cathode was 20% PTFE with 80 wt% activated carbon, whereas for the catalyzed electrode
it was 20 wt% PTFE with 76 wt% activated carbon and 4 wt% CeO
2.
Electrolyte composition
[0082] Independent electrodes were tested as gas-diffusion cathodes, in presence of air
or N
2 respectively, at the cathodic gas compartment. CeN
3O
9 ·6H
2O was added to the cathodic electrolyte, composed of 30 g/L NaCl and 10 mM sodium
acetate dissolved in demineralized water and adjusted at pH 2.7 with HCl. Different
concentrations of CeN
3O
9 ·6H
2O were independently tested, as follows: 0 ppm, 100 ppm, 500 ppm, 1000 ppm, 2000 ppm,
3000 ppm, 5000 ppm and 10000 ppm. The electrolyte at the counter-electrode (anode)
compartment remained the same, but without the addition of Ce. The experiments were
carried out at room temperature (18±2 °C).
Electrochemical operation and characterization
[0083] A Bio-Logic VMP3 potentiostat/galvanostat and frequency response analyzer was used
in order to perform the electrochemical measurements. EC-Lab v.10.23 software was
used for data acquisition. Chronoamperometric experiments were carried out at -0.350
V vs the reference electrode during a period of 120 min. Within that period steady
state was achieved. Electrochemical Impedance Spectroscopy (EIS) and Cyclic Voltammetry
(CV) were registered before and after the polarization, in order to indirectly evaluate
the effectiveness of the metal recovery process.
[0084] During the CA experiments at -0.350 V the production of H
2O
2 after O
2 electrochemical reduction takes place with the electrodes and electrolyte here proposed.
At these conditions, electrodeposition of metallic Ce is not expected, as the thermodynamic
condition for Ce reduction in aqueous medium within the pH range here studied (as
shown in the Pourbaix diagrams) would happen only at potentials lower than -2.7 V
[Pourbaix, 1974]. Still, transport of dissociated Ce
3+ ions towards the cathode is expected, with possible subsequent adsorption in the
porous electrode active sites. Otherwise, water electrolysis to form hydrogen is not
expected at the conditions of the study.
[0085] Electrochemical Impedance Spectroscopy (EIS) was recorded at the steady state polarization
potential (-0.350 V) a frequency range from 3 kHz to 3 mHz, with 6 points per logarithmic
decade, using an amplitude of 10 mV. Careful attention was paid to guarantee stability,
linearity, causality and finiteness, so that reliable and valid impedance data were
obtained. The EIS response was only recorded when the variation of current was detected
to be < ±10 µA during a period of at least one hour. The time of a whole impedance
scan was of about 19 minutes. Linearity was verified by real time monitoring of non-distortions
in Lissajous plots, which were observed via an on-line connected oscilloscope. Causality
was ensured as spurious (noisy) data were not observed while recording EIS. Validity
of the data was verified by using the Kramers-Kronig transforms. After the corresponding
EIS measurements, CVs were recorded in 2 cycles at 1 mV s-1, in a potential range
from -0.450 to 0.450 V
us Ag/AgCl. Only the second cycle of the CV is here reported. No IR drop correction
was established for the experiments here performed.
Analysis of the concentration of H2O2
[0086] A spectrophotometric method was employed to determine the concentration of
H2O2 in solution as disclosed by Aryal & Liakopoulou-Kyriakides 2013, 3:117. Reagent A
was prepared by mixing 33 g KI, 1 g NaOH and 0.1 g (NH
4)
6Mo
7O
24·4H
2O into 500 mL deionized water. This solution was kept in dark conditions to inhibit
oxidation of I. Reagent B was prepared with 10 g KHP dissolved into 500 mL deionized
water. The standard calibration curve (not shown) was prepared from known H
2O
2 concentrations from 0 to 3 mg L
-1, dissolved into the same electrolyte used for the experiments, without cerium. Further
analysis was carried out by pipetting 3.0 mL of Reagent A, 3.0 mL of Reagent B and
3.0 of standard sample into a beaker. The content of the mixture was allowed to react
for 5 minutes, before reading the absorbance of the solution at 351 nm [
GSI Scientific Report. (2009) Helmholtzzentrum für Schwerionenforschung, 2010-1].
[0087] The concentrations calculated of H
2O
2 are the average of the quantitative results obtained with 5 averaged calibration
curves, described by the following equation :

[0088] Where C
H2O2 refers to the concentration of hydrogen peroxide (mg L
-1) and A
351 denotes the absorbance registered at 351 nm.
[0089] Beside the known concentrations, problem samples were obtained after the electrochemical
characterization experiments and were analyzed through the same procedure as the standards.
X-ray diffraction
[0090] X-ray powder diffraction (XRD) experiments were carried out using diffractometer
PANalytical X'Pert Pro with CuKα (X = 1.5405Å) at 40kV. The conditions were: 4sec/step;
step = 0.04° and continuous scan. The wet precipitates were placed on a monocrystal.
The samples were measured both wet and dry. Since there were no important variations
between them only the values concerning the dry samples are reported here.
[0091] The identification of the crystalline phases was done by comparison with the database.
The crystallite size (D) was calculated using Scherrer's equation (Eq. 8):

where
B is the Scherrer constant (0.89), λ is the wavelength of the X-ray beam (1.5405Å),
β1/2 is the full width at half maximum of the diffraction peak and
θ is the diffraction angle.
[0092] Independent aqueous solutions with fixed concentrations of NaCl and sodium acetate
(CH
3COONa) were supplemented with varying concentrations of Ce(NO
3)
3 ·6H
2O (namely 0 mg.L
-1, 100 mg.L
-1, 500 mg.L
-1, 1000 mg.L
-1, 2000 mg.L
-1, 3000 mg.L
-1, 5000 mg.L
-1, and 10000 mg.L
-1, respectively). The pH of each electrolyte was fixed at 2.7, with HCl. A colourless
solution was formed in all cases. A constant potential of -0.350 V vs Ag/AgCl (3M
KCl) was applied to the said cathodes. At the gas-compartment, N
2 or air were supplied for each independent experiment, at a constant flow rate (∼400
mL.min
-1). Under such operational conditions water electrolysis is avoided; however, when
air is supplied through the GDE, O
2 electrochemically reduces to H
2O
2, upon availability of protons and electrons [Yang et al., 2000; Zhimin et al., 2001[RS1]].
[0093] The overall solution was considered to be electroneutral before the electrochemical
polarization was applied. Given the high concentration of NaCl, ion transport by migration
is unlikely to occur.
[0094] As soon as the electrical polarization was applied to the cathode, a gradient of
electrochemical potential developed across the half-cell. Since the concentration
gradients were initially absent, the transport of some positively charged ions was
likely steered from the solution in equilibrium towards the surface of the porous
cathode, which were thus captured by potential-modulated electrosorption and stored
capacitively in the diffuse part of the electric double layer.
[0095] Figure 2 shows the extent of transport of the Ce
3+ ions (removal efficiency in %) from the bulk solution in the presence of N
2 supplied through the gas-diffusion cathode and in the absence of oxidant gas. The
removal efficiency (%) was calculated as a function of the initial content of Ce
3+ in solution (Ce
T,i / mg):

Ce
T,f (mg) stands for the final content of Ce
3+ in solution.
[0096] When no Ce
3+ was supplied in the aqueous matrix (0 ppm), as a consequence of the starting concentration
gradient established, the transport of Na
+ within the porous electrode microstructure may have been prolonged by diffusion to
the rest of the electrode porosity. Yet, Na
+ was available at its highest concentration in the bulk. Altogether this establishes
diffusion from the bulk to the EDL in the overall porosity of the GDE as the rate
limiting step for Na
+ transport, until a dynamic equilibrium was reached.
[0097] Figure 3 shows the electrochemical response obtained for the experiments where no
oxidant gas was supplied through the gas-diffusion electrode and only N
2 was provided. Fig. 3a : Frequency response obtained by Electrochemical Impedance
Spectroscopy (EIS) recorded at 20 mV amplitude, in the frequency range from 100 kHz
to 3 mHz. Fig. 3b shows the cyclic voltammetry response obtained at a scan rate of
1 mV.s
-1. Fig. 3c and d shows typical EIS responses for diffusional limitation across a film
of infinite thickness (left) and limitations by finite diffusion through a film with
fixed amount of electroactive substance, which once consumed is not replenished at
the electrode or is only replenished very slowly (right). Fig. 3e shows a typical
capacitive and pseudo-capacitive CV responses.
[0098] In figure 3, the symbols given below relate to the indicated experiments:
○ ti, CCe3+,i = 0 mg.L-1 Ce3+.
● tf, CCe3+,i = 0 mg.L-1 Ce3+.
Δ t0, CCe3+,i = 10 g.L-1 Ce3+.
▲ tf, CCe3+,i = 10 g.L-1 Ce3+.
[0099] The frequency response for this case, obtained by electrochemical impedance spectroscopy
(EIS) was found to be typical of semi-infinite linear diffusion (see Fig. 3a), this
is, unrestricted diffusion to the large porous cathode. In the high frequency range,
EIS presented a shift from a typical constant phase element behaviour (at the beginning
of the experiment) to a pseudo-transfer resistance behaviour (at the end of the experiment)
which is characteristic of the occluded porosity [
Kaiser et al (1976) Electrochim. Acta, 21, 539]. The response in cyclic voltammetry (see Fig. 3b) is characteristic of porous electrodes
with pseudo-capacitive behaviour (see Fig. 3c), which confirms the capacitive storage
of Na
+ [
Yang et al., 2003, J Electroanal Chem 540:159]; yet, the overall process is limited by diffusion. Although some Na
+ is indeed considered to be electrostatically adsorbed, virtually no changes were
observed on its bulk concentration (seen as conductivity) due to the proportion between
the small quantity of ions that can be actually electrosorbed at the EDL and those
exceedingly available in the aqueous matrix.
[0100] Conversely, for the cases supplemented with Ce
3+ (4 mg to 403 mg of Ce
3+, corresponding to the aforementioned concentrations of Ce(NO
3)
3 from 100 ppm to 10000 ppm) the frequency response was observed to be distinctive
of limitations by finite diffusion through a film with fixed amount of electroactive
substance, which once consumed is not replenished at the electrode or is only replenished
very slowly (see Fig. 3a.
[0101] Although Fig. 3 only presents the EIS and CV data obtained for the systems without
Ce(No
3)
3 ·6H
2O or those supplemented with 10 g.L-1 of Ce(NO
3)
3 ·6H
2O, the electrochemical behaviour is representative of all cases where N
2-flows at the cathodic gas compartment and where the electrolyte is supplemented with
Ce
3+ even at concentrations as low as 100 mg.L-1 of Ce(NO
3)
3·6H
2O.
[0102] The pH and conductivity were monitored at the catholyte, at the start and end of
the experiments. For the cases where N
2 was supplied (Finding 1) the starting pH of 2.7 for each individual experiment increased
in about 0.3±0.18 by the end of the experiments, whereas it slightly decreased as
a function of concentration (in no case it decreased below 2.8±0.2). The starting
conductivity for the case without Ce
3+ (i.e. 30 g.L
-1 NaCl + 10 mM sodium acetate) was 49.7±0.6 and it remained quasi-stable by the end
of the experiments (50.1±0.3). This shows that practically no variation in the concentration
of NaCl could be achieved at such high NaCl concentrations. For the cases with Ce
3+, an ordinary increase of the conductivity was observed as a function of concentration,
before polarization. In this case, the conductivity decreased slightly after the polarization
treatment was applied, in good agreement with the removal efficiencies observed in
Figure 2; this is, by the end of each experiment the conductivity approximately corresponded
to that of the 30 mg.L
-1 NaCl alone.
[0103] For the system where N
2 was passed through the GDE the average Ce
3+ removal efficiency was 25.42 ±12.14% (see Fig. 2). In the absence of oxygen or other
oxidant gases the removed amount of metal ions (Ce
3+) is believed to be captured at the porous electrode structure mostly by ion-exchange
at the surface functionalities which contained Cl, S and O groups as characterized
by scanning electron microscopy and energy dispersive X-ray spectroscopy.
O2 supplied as the oxidant gas through the gas-diffusion cathode
[0104] VITO CORE™ cold-rolled gas-diffusion electrodes (GDE), made of porous activated carbon
(NORIT SX 1G), were employed as. The specific surface area for the powder of which
the electrodes are made is of about 1000 m
2.g
-1. Once shaped in the form of the porous electrode, the active carbon layer typically
has a specific surface area as measured according to the BET method of between 621
m
2.g
-1 to 745 m
2.g
-1 (
Alvarez-Gallego et al 2012 Electrochim Acta 82:415,
Sharma et al., 2014 Electrochimica Acta 140 191)
[0105] Figure 4 shows the extent of transport of the Ce
3+ ions (removal efficiency %) from the bulk solution in the presence of O
2 as the oxidant gas supplied through the gas-diffusion cathode and flowing through
the gas compartment and diffusing through the gas-diffusion electrode. In this case,
about the entire amount of Ce
3+ was removed from solution (average 99.47±0.53%), as shown in Fig. 4. Contrary to
the previous case, the removal efficiency does not increase as a function of the concentration
of metal in solution, indicating that adsorption by ion-exchange is not the prevailing
phenomenon as in a classical electrosorption case (see finding 1).
[0106] The removal efficiency when O
2 was supplied through the gas-diffusion cathode was much more significant than in
the case where only N
2 was supplied.
[0107] Not only removal of Ce
3+ ions from solution took place but also the formation of a stable solid phase. Figure
5 shows the recovery efficiency (%) of the Ce
3+ ions transformed into a solid product recovered as precipitate after being released
from the electrode and sedimented in solution, in the presence of O
2 as the oxidant gas supplied through the gas-diffusion cathode, on the basis of dry
weight of the recovered product.
[0108] The solid phase is composed of CeO
2 isotropic nanocrystals, as identified by XRD and microscopic evidence described later,
which precipitated at the interface between the porous activated carbon gas-diffusion
electrodes (GDE) and the adjacent aqueous electrolyte. These were initially identified
as colloidal nano particles dispersed in solution, which aggregate and precipitate
as the process keeps running. Some of these are released into the bulk electrolyte
whereas others stay attached to the electrode and are only released after stopping
or reverting the electric polarization.
[0109] Higher recovery percentages were obtained at lower Ce
3+ concentrations. It should be noted that the low recovery efficiencies are not due
to low conversion rates. The discharge of the crystalline nano particles was not done
by other means than just reversing the flow. Those nano particles that could be collected
within that reversal time are those which were quantified. In this case, polarization
reversal increases recovery.
[0110] The intermediates, byproducts (e.g. an adsorbed form of superoxide
O2•-(ads)) and the electrosynthesized H
2O
2 are believed to also play a role. The EIS behaviour was found to be typical of faradic
reactions (charge transfer) coupled by adsorbed intermediates (
Wu et al 2012 Chem Rev, 112:3959), as observed in Fig. 6a. The CV response (Fig. 6b) further indicated that the limiting
process at the GDE at -0.350 V vs Ag/AgCl were not anymore capacitive ion-storage
or electrosorption alone but an electrocatalytic reduction, presumably O
2 reduction to H
2O
2.
[0111] Figure 6 shows the electrochemical response obtained for the experiments where air
was supplied through the gas-diffusion electrode :
Fig. 6a shows the frequency response obtained by Electrochemical Impedance Spectroscopy
(EIS) recorded at 20 mV amplitude, in the frequency range from 100 kHz to 3 mHz.
Fig. 6b shows the cyclic voltammetry response obtained at a scan rate of 1 mV.s-1.
Fig 6c and d show typical EIS responses for adsorption limited processes linked to
charge transfer reactions.
[0112] The symbols in fig. 6 have the following meaning :
○ ti, CCe3+,i = 0 mg.L-1 Ce3+.
● tf, CCe3+,i = 0 mg.L-1 Ce3+.
Δ t0, Cce3+,i = 10 g.L-1 Ce3+.
▲ tf, CCe3+,i = 10 g.L-1 Ce3+.
[0113] Figure 7 shows the crystallite size and lattice parameter found for the different
initial Ce
3+ concentrations studied.
[0114] Figure 7a shows the crystallite size (220) for CeO
2 and NaCl.
[0115] Figure 7b shows the lattice parameter CeO
2 and NaCl. There was a limit in detection for both parameters at Ce below 20 mg.
[0116] The crystal size of the crystalline product varied in gradient as a function of the
initial concentration of Ce
3+, but also proportionally to the concentration of H
2O
2 found in solution (Figure 7a). At lower Ce
3+ concentrations the crystal size of CeO
2 is smaller whereas as the concentration increases the crystal size is larger. The
average crystal size for CeO
2 was 3.5±0.337 nm, whereas for NaCl it was 45.1275±0.337. This makes possible further
separation either by re-dissolution of NaCl with a pH where CeO
2 is still stable, e.g. pH >10 or by size exclusion (e.g. screening) after drying.
The lattice parameters observed in Fig 7b, also varied as a function of initial Ce
3+ ion concentration and proportionally to the concentration of H
2O
2 found in solution. It is possible that Ce
3+ plays a co-catalytic role in the electrosynthesis of H
2O
2 itself.
[0117] Figure 8 shows transmission electron micrographies evidencing the characteristic
morphology of CeO
2 nano particles with crystallite sizes matching those obtained by XRD.
[0118] Figure 9 shows transmission electron micrographies evidencing the aggregation of
the small crystalline nano particles of Figure 8 into larger size nano particles.
[0119] Fig. 8 and 9 in fact show characteristic fingerprints of the materials formed by
the method of this invention, whose properties can be tuned as per controlled variations
in the physicochemical or electrochemical conditions provided.
EXAMPLE 2.
[0120] Independent electrodes were tested as gas-diffusion cathodes, in presence of air
at the gas compartment (to provide O
2 for its reduction to H
2O
2, its polyatomic ions or radical). The reagents presented in Table A were dissolved
in demineralized water and the pH of the solution where the pH was adjusted to approximately
4.
Table A: Composition of catholyte in demineralized water.
| |
Chemical name |
Chemical formula |
Quantity (mg.L-1) |
| 1 |
Cerium nitrate hexahydrate |
Ce(NO3)3 · 6H2O |
350 |
| 2 |
Dysprosium nitrate x hydrate |
Dy(NO3)3·xH2O |
80 |
| 3 |
Erbium nitrate pentahydrate |
Er(NO3)3·5H2O |
53 |
| 4 |
Europium nitrate pentahydate |
Eu(NO3)3· 5H2O |
6 |
| 5 |
Gadolinium nitrate hexahydrate |
Gd(NO3)3· 6H2O |
59 |
| 6 |
Holmium nitrate pentahydrate |
Ho(NO3)3· 5H2O |
18 |
| 7 |
Lanthanum nitrate hexahydrate |
La(NO3)3· 6H2O |
159 |
| 8 |
Lutetium nitrate hydrate |
Lu(NO3)3·xH2O |
6 |
| 9 |
Neodymium nitrate hexahydrate |
Nd(NO3)3· 6H2O |
206 |
| 10 |
Praseodymium nitrate hexahydrate |
Pr(NO3)3·6H2O |
51 |
| 11 |
Samarium nitrate hexahydrate |
Sm(NO3)3· 6H2O |
53 |
| 12 |
Terbium nitrate hexahydrate |
Tb(NO3)3· 6H2O |
12 |
| 13 |
Thulium nitrate pentahydrate |
Tm(NO3)3· 5H2O |
8 |
| 14 |
Yttrium nitrate hexahydrate |
Y(NO3)3·6H2O |
536 |
| 15 |
Ytterbium nitrate pentahydrate |
Yb(NO3)3· 5H2O |
50 |
Additionally, 30 g/L NaCl were provided and dissolved. The operational volume of the
catholyte in each experiment was 125 mL.
[0121] The concentration of the different metals was quantitatively analyzed by means of
ICP-MS.
[0122] The process was applied at constant polarization at -0.350 mv vs the previously referred
reference electrode for a period of 2 hours. After few minutes of processing (<20
min), the color of the electrolyte progressively shifted from transparent towards
white in one appreciable turbid phase. The process showed a gradual change in pH up
to 11. Current densities above 40 mA.cm
-2 were registered under the constant cathodic polarization conditions. After the process
was stopped, the solid particles formed aggregated and sedimented leaving a clear
liquid medium and a separable solid precipitate phase.
[0123] Most of the metal content was found to be removed from solution (Figure 10), this
is, >99.9 for all metals together, as determined by ICP-MS.
[0124] Figure 10 shows the removal efficiency (%) of the different metal ions from the bulk
solution in the presence of air supplied through the gas-diffusion cathode.
[0125] A mixed crystalline concentrate was obtained. In total, 91 mg of solid REE content
were recuperated which correspond to about 25% of the total ionic (dissolved) REE
content in the original aqueous matrix. The isolated products showed crystalline properties
matching with crystallite sizes of 1.97 nm, 1.71 nm and 2.29 nm, respectively.
EXAMPLE 3.
[0126] The composition of the electrolyte was identical to that explained for example 1,
but lanthanum nitrate was used instead of cerium nitrate, in concentrations of 0 ppm,
100 ppm, 500 ppm, 1000 ppm and 5000 ppm.
[0127] The initial pH and conductivity of the catholytes containing the different concentrations
of the metal are disclosed in Table b. The operational volume of the catholyte in
each experiment was 125 mL.
Table b: Measured pH and conductivity of the catholytes with different concentrations
of lanthanum nitrate La(NO
3)
3·6H
2O by the start of experimentation.
| |
Concentration (ppm) |
0 |
100 |
500 |
1000 |
5000 |
| Catholyte |
pH |
2.54 |
2.15 |
2.70 |
2.78 |
2.76 |
| Conductivity (mS.cm-1) |
51.0 |
51.6 |
50.4 |
50.3 |
52 |
| Anolyte |
pH |
2.8 |
2.8 |
2.74 |
2.74 |
2.74 |
| Conductivity (mS.cm-1) |
49.7 |
49.7 |
49.8 |
49.8 |
49.8 |
[0128] The concentration of lanthanum was quantitatively analyzed by means of ICP-MS.
[0129] A colourless solution was formed when dissolving the chemicals. Air was supplied
to the gas compartment. After 2 h of processing at constant polarization conditions
of -0.350 V vs Ag/AgCl (3M KCl), the color of the electrolyte remained transparent
throughout the experiment. However when stopping the polarization and reversing the
flow, visible white turbidity was released into the medium. The amount of product
released (or turbidity) corresponded to the initial concentration of lanthanum nitrate.
After about an hour, all the turbid product had precipitated. The pH changes were
similar to those observed in the catholyte in example 1, the pH of the catholyte significantly
increased by the end of the experiments where air was supplied through the gas diffusion
compartment. The conductivity and pH of catholyte and anolyte, remained almost the
same. An overall slight decrease in catholyte conductivity could be debated.
Table c: pH and conductivity of the catholytes for different concentrations of La(NO
3)
3·6H
2O at the end of the experiment.
| |
Concentration (ppm) |
0 |
100 |
500 |
1000 |
5000 |
| Catholyte |
pH |
11.5 |
12.47 |
11.62 |
11.8 |
5.37 |
| Conductivity (mS.cm-1) |
49.1 |
49.9 |
51.6 |
50.7 |
47.4 |
| Anolyte |
pH |
2.37 |
2.78 |
2.23 |
2.20 |
2.68 |
| Conductivity (mS.cm-1) |
49.7 |
49.9 |
50.7 |
49.5 |
47.5 |
The clear solution and the solid white precipitate were separated and analyzed. For
all cases >99.9% of lanthanum had been removed from the solution. When analyzing the
white precipitate by XRD, the produced solid showed characteristics of crystalline
nano particles matching those of burbankite and more specifically lanthanum remondite,
this is Na
3La
3(CO
3)
3. An amorphous phase was additionally detected.
EXAMPLE 4.
[0130] The composition of the electrolyte was identical to that explained for example 1
but instead of cerium nitrate a boric acid was supplied in the catholyte. The concentration
of boric acid was kept constant for all experiments (5 g.L
-1). The effect of the polarization potential was evaluated. The following potentials
vs. the reference electrode were compared: -0.350 V, - 0.550 V, -0.750 V, -0.950 V.
The operational volume of the catholyte in each experiment was 125 mL.
Table D: pH and conductivity of the catholyte at the start of experimentation at different
cathode potentials.
| |
Applied potential (V vs Ag/AgCl 3 M KCl) |
-0.150 |
-0.350 |
-0.550 |
-0.750 |
-0.950 |
| Catholyte |
pH |
2.67 |
2.63 |
2.51 |
2.51 |
2.76 |
| Conductivity (mS.cm-1) |
47.1 |
47.4 |
47.2 |
47.4 |
46.9 |
| Anolyte |
pH |
2.74 |
2.74 |
2.8 |
2.8 |
2.8 |
| Conductivity (mS.cm-1) |
49.8 |
49.8 |
49.7 |
49.7 |
49.7 |
[0131] From the changes in the pH and conductivity, especially of the catholyte, it can
be observed that the same trend found in previous examples was observed; this is,
the pH significantly increased throughout the experiment. However, only in the case
at -0.950 V a visible colour change of the electrolyte towards yellow could be observed.
[0132] The shift in pH was directly correlated to the applied potential. The pH change took
place during the first hour of the experiment and even increasing further the time
of polarization (i.e. from 2 to 4 h) did not result in pH variations to higher magnitudes.
Table E: Measured pH and conductivity of the catholytes by the end of experimentation
at different applied cathode potentials.
| |
Applied potential (V vs Ag/AgCl 3 M KC1) |
-0.150 |
-0.350 |
-0.550 |
-0.750 |
-0.950 |
| Catholyte |
pH |
5.37 |
6.55 |
6.92 |
8.45 |
8.5 |
| Conductivity (mS.cm-1) |
45.2 |
46.6 |
46 |
44.1 |
45 |
| Anolyte |
pH |
2.68 |
2.13 |
2.15 |
2.13 |
2.15 |
| Conductivity (mS.cm-1) |
47.5 |
51.0 |
50.3 |
50.5 |
50.8 |
After centrifugation and drying, a crystalline product matching the characteristics
of sassolite could be recuperated.