The lanthanides (Ln) are an essential part of many advanced technologies. Our societal transformation toward renewable energy drives their ever-growing demand. The similar chemical properties of the Ln pose fundamental difficulties in separating them from each other, yet high purity elements are crucial for specific applications. Here, we propose an intralanthanide separation method utilizing a group of titanium(IV) butyl phosphate coordination polymers as solid-phase extractants. These materials are characterized, and they contain layered structures directed by the hydrophobic interaction of the alkyl chains. The selective Ln uptake results from the transmetalation reaction (framework metal cation exchange), where the titanium(IV) serves as sacrificial coordination centers. The "tetrad effect" is observed from a dilute Ln3+ mixture. However, smaller Ln3+ ions are preferentially extracted in competitive binary separation models between adjacent Ln pairs. The intralanthanide ion-exchange selectivity arises synergistically from the coordination and steric strain preferences, both of which follow the reversed Ln contraction order. A one-step aqueous separation of neodymium (Nd) and dysprosium (Dy) is quantitatively achievable by simply controlling the solution pH in a batch mode, translating into a separation factor of greater than 2000 and 99.1% molar purity of Dy in the solid phase. Coordination polymers provide a versatile platform for further exploring selective Ln separation processes via the transmetalation process.
The lanthanides (Ln) are an essential part of many advanced technologies. Our societal transformation toward renewable energy drives their ever-growing demand. The similar chemical properties of the Ln pose fundamental difficulties in separating them from each other, yet high purity elements are crucial for specific applications. Here, we propose an intralanthanide separation method utilizing a group of titanium(IV) butyl phosphate coordination polymers as solid-phase extractants. These materials are characterized, and they contain layered structures directed by the hydrophobic interaction of the alkyl chains. The selective Ln uptake results from the transmetalation reaction (framework metal cation exchange), where the titanium(IV) serves as sacrificial coordination centers. The "tetrad effect" is observed from a dilute Ln3+ mixture. However, smaller Ln3+ ions are preferentially extracted in competitive binary separation models between adjacent Ln pairs. The intralanthanide ion-exchange selectivity arises synergistically from the coordination and steric strain preferences, both of which follow the reversed Ln contraction order. A one-step aqueous separation of neodymium (Nd) and dysprosium (Dy) is quantitatively achievable by simply controlling the solution pH in a batch mode, translating into a separation factor of greater than 2000 and 99.1% molar purity of Dy in the solid phase. Coordination polymers provide a versatile platform for further exploring selective Ln separation processes via the transmetalation process.
The lanthanide (Ln) series, collectively
made up of a group of 15 elements, has gained strategic importance
in recent decades. The unique 4f electron structures entail distinctive
and, in many cases, irreplaceable physical properties that make Ln
essential components in advanced electronics, lasers, and permanent
magnets.[1,2] Owing to the poor shielding of nuclear charge
by 4f electrons, Ln3+ ions share extremely similar yet
descending ionic radii across the series with an average difference
between adjacent elements of only 1 pm (Ln contraction).[3] Consequently, Ln forms isostructural mineral
compounds that are almost always found together in the geosphere.[4] Despite their considerably similar chemical characters,
the magnetic and optical properties of Ln differ, and as a result,
obtaining pure fractions of individual Ln is crucial for specific
applications. The efficient separation of Ln remains a challenging
task.Historically, fraction crystallization was adopted to
produce pure Ln.[5] This is proven to be
tedious and time-consuming because hundreds of cycles are required.
During the Manhattan project, ion-exchange chromatography utilizing
organic resins was developed to separate Ln and actinides.[6] The difficulties in continuous operation and
resin regeneration restricted its further scalability. Nowadays, continuous
liquid–liquid extraction (solvent extraction) is the state-of-the-art
technology for Ln separation on an industrial scale.[6] The separation is enabled by complex-forming extractants
that selectively transfer the Ln ions from the aqueous to organic
phases. Nevertheless, the inevitable liquid waste generation in the
solvent extraction process has resulted in a search for more environmentally
friendly separation methods.[7]Recent
advances in f-element coordination chemistry have reopened the window
for selective crystallization, (bio)mineralization, and supramolecular
self-assembly.[8−14] The small difference in ionic radii can be amplified during the
crystallization with desirable multidentate ligands, resulting in
metal–organic framework (MOF) materials with fine-tuned sizes,
shapes, and crystal structures.[15] Often,
these processes are energy-intensive because they are carried out
hydrothermally. Biomineralization is active under milder conditions,
yet the stability and reusability of artificial peptides are not satisfactory.
Another approach—solid-phase extraction—completely eliminates
the organic phase in solvent extraction. Organic–inorganic
hybrid materials utilizing an array of inorganic porous supports and
organic functional ligands have been developed for selective Ln sorption.[16−20] Recently, we have shown that titanium alkyl-phosphate functionalized
mesoporous silica possesses solvating extraction capability.[21] The surface alkyl chains linked to titaniumphosphate moieties mimic the structure of tri-n-butyl
phosphate (TBP) and hence form complexes with Ln nitrates. However,
these materials seem not to be perfect candidates for intralanthanide
separation because of the similar complex formation constants across
the Ln series.Inorganic ion exchangers, namely, metal(IV) phosphate
materials, are used for selective metal separation and decontamination.[17,22,23] Purely inorganic titanium[24] and zirconium phosphate[25] (TiP and ZrP) materials were studied for rare-earth separation via
cation exchanges with the proton in the hydrogenphosphate groups.
This reversible extraframework cation exchange reaction does not disrupt
the building blocks of the material, and therefore the metal selectivity
is primarily based on ion-sieve selection and phosphate coordination.
Whereas inorganic phosphate offers limited Ln selectivity, simple
organic phosphoric acids [e.g., di-n-butyl phosphoric
acid (HDBP)[26] and di(2-ethylhexyl)-phosphoric
acid (DEHPA)[27,28]] demonstrate more promising intralanthanide
separation potentials. The ratio of the solubility product constants
(Ksp) between Dy(DBP)3 and
Nd(DBP)3 is reported to be more than 4000 (DBP is the deprotonated
form of HDBP).[26] Titanium(IV) forms insoluble,
layer-structured precipitates with DBP in the form of a coordination
polymer.[29] The resultant material is composed
of alternating bilayers of butyl chains and titanium(IV) phosphate.
Although titanium(IV) and zirconium(IV) phosphonates were intensively
studied,[30,31] there has been extremely limited information
regarding the properties and application of titanium(IV) organophosphate
materials in metal separation.In the present work, we describe
the synthesis and characterization of layered titanium(IV) butyl phosphate
materials and their uptake behavior toward Ln3+ ions. Contrary
to what we observed from the surface alkyl-phosphate grafted materials,
the titanium(IV) butyl phosphate materials do not retain Ln3+ in a solvating extraction manner. Instead, the driving force for
Ln3+ uptake originates from transmetalation reactions [framework
Ti(IV) exchange]. Significant group separation was achieved for early
and late Ln. This observation forms the basis of a Ln separation strategy
that combines both the high selectivity from the crystallization method
and the operational convenience from solid-phase extraction.
Experimental Section
Chemicals
Titanium(IV)
tetrachloride (TiCl4, >97%) and HDBP (>97%) were
purchased from Sigma-Aldrich. Lanthanide (including La, Ce, Pr, Nd,
Eu, Gd, Tb, Dy, Yb, and Lu) solutions were prepared from their corresponding
nitrate salts (>99.9%, Sigma-Aldrich). ortho-Phosphoric
acid (>99.9%) and ethanol (>99.5%) were purchased from VWR Chemical.
For metal (uptake) analysis, elemental standard solutions (1000 mg
L–1, PrimAg-plus cert. ref. material) and nitric
acid (SpA super purity, 67–69%) were obtained from ROMIL (Cambridge,
UK). Ultrapure water (Milli-Q, Millipore) with a resistivity of 18.2
MΩ cm was used.
Synthesis of the TiP Materials
A
precipitation method was employed for the synthesis of the TiP materials.
By carefully dissolving TiCl4 in water under vigorously
stirring (1000 rpm, ∼1 h), a completely transparent Ti(IV)
precursor solution (1 M) was obtained. A series of phosphate precursor
solutions (0.2 M total P) was prepared by diluting different amounts
of 85% H3PO4 and HDBP into a 50/50 (v/v) water/ethanol
mixture, with the final H3PO4-to-HDBP molar
ratios at 1:0, 3:1, 1:1, 1:3, and 0:1. The precipitation reaction
was carried out by the dropwise addition of 10 mL of the Ti(IV) precursor
into 100 mL of the phosphate precursors while stirring (1000 rpm).
Note that the P/Ti molar ratio in all synthesis liquors was fixed
to 2. The suspension was aged at room temperature for 1 h under the
same stirring condition. The resulting white slurry was then washed
three times with the water/ethanol mixture through centrifugation
(2 min, 5000g) and redispersion. Finally, the materials
obtained were air-dried at 60 °C in an oven overnight. The materials
synthesized from the phosphate precursors with different inorganic-to-organic
phosphate ratios were denoted as TiP_x/y, where x/y = n(H3PO4)/n(DBP) = 1:0, 3:1,
1:1, 1:3, and 0:1 (Table ). All of them were ground and sieved to a particle size between
74 and 149 μm (100–200 mesh) before further study.
The powder X-ray diffraction (XRD) patterns in the Bragg–Brentano
geometry were recorded by a PANalytical X’Pert3 PW3710 MPD
diffractometer control unit, a PW3020 vertical goniometer, and a monochromatic
Cu Kα radiation source (λ = 1.54056 Å) operated at
40 kV and 40 mA.
Infrared Spectroscopy
Infrared (IR)
spectra (650–4000 cm–1) were recorded on
a PerkinElmer Spectrum One Fourier transform infrared (FTIR) spectrometer
equipped with a Universal attenuated total reflection (ATR) sampling
accessory.
Raman Spectroscopy
Raman spectra
were recorded using a confocal Raman microscope (NTEGRA Spectra, NT-MDT)
in the 100-to-1200 cm–1 region with a spectral resolution
of 2 cm–1. The measurements were performed with
a 532 nm Nd:YAG laser (output power 20 mW) and a 100× objective.
The acquisition time was typically 1 min. We checked that the laser
light did not damage the sample.
Surface Area
The
Brunauer–Emmett–Teller (BET) surface area and porosity
of the materials were determined at 77 K by the nitrogen (N2) adsorption–desorption method (TriStar II Plus, Micromeritics),
and the samples were degassed at 150 °C for 5 h prior to the
measurements (VacPrep 061 degassing unit).
Scanning Electron Microscopy
The surface morphology of the TiPs was observed using a Hitachi
S-4800 FE-SEM (field-emission scanning electron microscopy) after
they were sputter-coated with a 3 nm layer of Pd–Au alloy.
Compositional Analysis
The elemental contents (C and H)
were analyzed using a Thermo Scientific Flash 2000 elemental analyzer.
The contents of Ti and P were determined by a PerkinElmer Optima 8300
inductively coupled plasma optical emission spectrometer (ICP-OES)
after total digestion in 65% HNO3 and 1% HF using a CEM
MARS 5 microwave digestion system.
Thermogravimetry
The simultaneous thermogravimetry and differential scanning calorimetry–mass
spectroscopy (TG/DSC–MS) analysis was performed using a simultaneous
TG/DSC apparatus (STA 449F3 Jupiter, Netzsch) connected to a JAS-Agilent
GC–MS (7890B GC/MSD5977A). In the dynamic TG measurements,
the samples were heated from 30 to 800 °C at a heating rate of
20 °C min–1 under a helium gas flow of 40 mL
min–1.
Solid-State Nuclear Magnetic Resonance
The solid-state 13C and 31P magic-angle spinning
(MAS) nuclear magnetic resonance (NMR) spectra were collected on a
Bruker AVANCE III 500 MHz spectrometer equipped with a 4 mm H/X/Y
MAS probe. The samples were filled in a 4 mm zirconia rotor and measured
at a MAS rate of 12 kHz. 13C spectra were recorded with 1H–13C cross-polarization (CP) pulse sequence,
2048 scans, a recycle delay of 5 s, spinal-64 1H decoupling,
and a contact time 0.5 ms. The spectra were referenced with respect
to adamantane at 38.5 ppm. 31P spectra were acquired with
a 90° pulse (77 kHz rf), a 100 s recycle delay, and 64 scans.
The 31P chemical shifts were referred to external 85% H3PO4 at 0 ppm.
Metal Concentration Determination
Determination of the metals was performed on an Agilent microwave
plasma-atomic emission spectrometer 4200. Depending on suitability,
one of Sc, La, or Fe was used as the internal standard for quality
control. Samples were diluted to concentrations below 25 mg L–1, and a linear calibration curve was established by
0, 0.5, 1, 2, 5, 10, and 25 mg L–1 standard solutions.
Ln3+ Uptake Study
The Ln3+ ion-exchange
extraction was studied in a batch mode. Typically, 50 ± 1 mg
of TiP material was placed in a polyethylene vial with 10 mL of Ln3+-containing solution. Samples were equilibrated for 48 h
(unless otherwise stated) by constant rotary mixing (50 rpm). The
solid/liquid separation was then achieved by filtering through a 0.22
μm poly(vinylidene difluoride) syringe filter, and the clear
solution was pipetted for concentration determination. Equilibrium
pH was measured from the remaining filtrate.The distribution
coefficient (Kd, mL g–1) demonstrates the distribution of a Ln element (or a group of selected
Ln elements) between the solution and the solid material. It was calculated
by eq :where is
the Ln3+ concentration in the solid (mg g–1) after the sorption, [Ln3+]i and [Ln3+]t are, respectively, the Ln3+ concentration
of the solution before and after sorption (mg L–1), respectively, V is the volume of the solution
(10 mL), and m is the mass of the material (0.05
g).The separation factor (SF) between two Ln3+ ions
or two groups of Ln3+ ions (Ln1 and Ln2) was subsequently calculated based on their Kd values (eq ):
Results
and Discussion
Synthesis and Characterization of the TiP
Materials
TiCl4 is prone to hydrolysis even in
acid media, and the stable species of titanium in our synthesis liquor
is TiO2+ (eq ), according to the Pourbaix diagram.[32]The TiO2+ cations are then polymerized to form (TiO)2 chains. Two kinds of phosphate
precursors were employed in the synthesis, inorganic ortho-phosphoric acid (H3PO4) and organic HDBP.
Pure inorganic TiPs are a group of −H2PO4 and/or −HPO4 containing proton-type ion exchangers,
which have been extensively studied.[33] The
addition of HDBP to the synthesis liquor introduced the butyl phosphate
functional groups onto the amorphous TiP assembly based on the inorganic
backbone (Ti–O–P) by condensation reactions. In our
work, among the TiP materials synthesized (Table ), TiP_1:0 is a purely inorganic material,
whereas TiP_0:1 should supposedly contain only DBP groups. The others
are categorized into organic–inorganic mixed TiPs.Inorganic
TiP_1:0 exhibited a typical amorphous phase with a broad low-intensity
powder XRD peak (Figure a). The addition of HDBP resulted in the evolution of a peak at 2θ
= 5.9–6.3°, which translates into an interlayer spacing
of 1.41–1.51 nm. This observation corresponds with an earlier
study and suggests that these materials contain self-assembled butyl
group layers stacked via van der Waals interactions.[29] Despite the layered structure, the material lacks long-range
periodic order. This is mainly due to the high reactivity of Ti(IV),
leading to the formation of octahedral Ti-oxo-clusters and consequently
amorphous coordination polymers. The high charge and polarizing power
of Ti(IV) contribute to the chemical stability of the coordination
polymer.[34] A similar situation applies
to Zr(IV).[31]
Figure 1
Characterizations of
the synthesized TiP materials. (a) Powder XRD patterns. (b) ATR–FTIR
spectra. (c) Raman spectra with crystalline α-TiP as a comparison.
(d) Nitrogen adsorption–desorption isotherms measured at 77
K. (e) SEM images (smaller magnification in the left column and higher
magnification in the right column).
Characterizations of
the synthesized TiP materials. (a) Powder XRD patterns. (b) ATR–FTIR
spectra. (c) Raman spectra with crystalline α-TiP as a comparison.
(d) Nitrogen adsorption–desorption isotherms measured at 77
K. (e) SEM images (smaller magnification in the left column and higher
magnification in the right column).The ATR–FTIR peaks (Figure b) centered at 2959, 2934, 2906, and 2874
cm–1 are assigned to the stretching vibration of
C–H in butyl groups. The 1465 cm–1 band represents
the deformation vibration of the same groups.[29] The IR absorptions at 1023 and 733 cm–1 are typical
vibrational modes for C–O–(P) in phase vibration and
P–O3 symmetrical stretching, respectively.[35] The water content characterized by the O–H
vibration at 1623 cm–1 becomes less evident with
the increased organic content, as the hydrophobicity increases. The
Raman spectra (Figure c) revealed additional information regarding the linkage between
tetrahedral PO4 and octahedral TiO6 groups.
The broad peaks at about 730 cm–1 in TiP_0:1, TiP_1:3,
and TiP_1:1 materials are assigned to the vibration of Ti–O–Ti
chains that contain nonbridging oxygen.[36−38] This peak moves toward
higher Raman shifts and becomes less evident in TiP_3:1 and TiP_1:0
samples, and it is completely absent in crystalline α-TiP. We
therefore infer that the heterocondensation between Ti–O–H
and P–O–H groups competes with the homocondensation
process for Ti–O–H during the synthesis. HDBP possesses
only one P–O–H group, whereas H3PO4 harbors three. Because we fixed the overall P/Ti molar ratio at
2, the homocondensation reaction is expected to be more evident in
the synthesis precursor with a higher amount of HDBP. In general,
the Raman spectra of the TiPs exhibit an amorphous nature without
any sharp peaks. The stretching vibrations of the isolated phosphate
groups (in the 1000 cm–1 region) are only observable
from TiPs with a higher inorganic phosphate content (TiP_1:0 and TiP_3:1).N2 porosimetry analysis showed that the TiP samples
have different textural characteristics, as summarized in Table . For the organic-containing
TiP materials except TiP_3:1, the N2 adsorption–desorption
isotherms (Figure d) are type II with very small hysteresis of type H3, suggesting
monolayer–multilayer adsorption and aggregation of particles
in these TiP materials. However, TiP_3:1 and purely inorganic TiP_1:0
sample gave a type IV(a) isotherm with a hysteresis in the p/p0 range of 0.45–1.0
and 0.7–1.0, respectively,[39] which
is associated with capillary condensation taking place in their respective
mesopores. In TiP_1:0, the hysteresis loop is H2(b), associated with
pore blocking, with larger size distribution of the next widths, whereas
in TiP_3:1, the change in hysteresis to type H3, due to aggregation
of particles. The addition of small amount of organophosphate (in
TiP_3:1) increased the surface area and decreased the average particle
size (Table ). As
a general trend, the BET surface area decreases drastically with the
synthetic addition of organophosphate. The TiP_0:1 sample has a strikingly
low surface area (1.2 m2 g–1), whereas
the inorganic amorphous TiP_1:0 sample presents a contrasting value
of 142 m2 g–1. The self-assembly of the
butyl groups into a lamellar format resulted in lower pore volume,
larger average pore diameter, and significant growth (aggregation)
of the particles. This is consistent with the morphological observation
by SEM images in Figure e. These TiP materials appear as irregular pellets that are connected
to each other. It is worth noting that the inorganic TiP_1:0 sample
exhibits irregularly shaped large lumps under microscopic observation.
The addition of small amount of organophosphate (in TiP_3:1) increased
the surface area and decreased the average particle size. The capillary
condensation of N2 shifts to lower relative pressure from
the TiP_3:1 to TiP_0:1 sample, reflecting a decrease in the pore volume
due to the introduction of organophosphate. The structural and morphological
design of the inorganic TiP materials would be beneficial when small
amounts of organophosphate are added as structural modifiers. Nevertheless,
this is not the target of the current work and would require further
and detailed investigation.
Table 2
Textural Parameters
of the Synthesized TiPs
sample
SBET (m2g–1)a
Vtotal (cm3g–1)b
Dpore (nm)c
Dparticle (nm)d
TiP_1:0
142
0.62
15.1
42.3
TiP_3:1
184
0.43
14.6
32.7
TiP_1:1
16.0
0.12
38.7
375.0
TiP_1:3
6.5
0.05
40.0
916.6
TiP_0:1
1.2
0.01
72.0
5168.2
SBET: BET surface area.
Vtotal: total pore volume estimated
from the desorption branch by the Barrett–Joyner–Halenda
(BJH) method.
Dpore: average pore diameter estimated from the desorption
branch by the BJH method.
Dparticle: average particle size calculated
by density functional theory.
SBET: BET surface area.Vtotal: total pore volume estimated
from the desorption branch by the Barrett–Joyner–Halenda
(BJH) method.Dpore: average pore diameter estimated from the desorption
branch by the BJH method.Dparticle: average particle size calculated
by density functional theory.In order to solve the formulae of the obtained TiP materials, an
array of supplementary characterizations was made. The carbon (C),
hydrogen (H), titanium (Ti), and phosphorus (P) contents were determined
by elemental analysis (EA) and total digestion. The thermogravimetric
analysis (TGA) (Figure a) weight loss at below 105 °C gave an estimate of the adsorbed
water contents (0–3%, Table ). Solid-state 13C CP MAS NMR (Figure b) was run to check
that all of the C was sourced from the organic DBP groups and there
was no residual solvent. In addition, solid-state 31P MAS
NMR with peak deconvolutions (Figure c) provided us the relative ratios between the −H2PO4 and −HPO4 groups. It is reported
that peaks with a 31P chemical shift at −5 to −9
ppm result from −H2PO4 groups, whereas
those at −15 to −22 ppm represent −HPO4 groups.[38] Peaks close to 1–2 ppm
are assigned to DBP based on our liquid NMR results. The detailed
peak positions and relative quantification of the inorganic phosphate
groups are present in Table . Although the synthesis precursor for TiP_0:1 consisted only
of HDBP, inorganic −H2PO4 groups were
found in the final TiP_0:1. For this, a partial hydrolysis of HDBP
in acid media would be a logical explanation.
Figure 2
Characterizations in
relation to formulae calculations. (a) TG curves (solid line and left y-axis) and DSC curves (dashed line and right y-axis). (b) 13C CP MAS NMR spectra. (c) 31P
MAS NMR spectra with peak deconvolutions. (d) Powder XRD patterns
of the calcined TiP materials compared with ICDD reference patterns.
(e) Raman spectra of the calcined TiP materials.
Table 3
Characterization Results Used for the Formulae Calculations
31P NMR peak fitting
TGA
EA
digestion
HPO4
H2PO4
DBP
mass loss %
material
C wt %
H wt %
P wt %
Ti wt %
ppm
%
ppm
%
ppm
105 °C
800 °C
TiP_1:0
0.1
2.8
15.1
27.5
–22.0,
−21.0
27.6
–7.7
72.4
2.6
19.6
TiP_3:1
12.7
4.2
15.2
24.0
–22.0, −21.7
45.2
–5.3, −11.1
54.8
0.5, 1.9
2.2
30.1
TiP_1:1
24.5
5.4
13.8
17.3
–21.7,
−18.7
46.4
–9.9
53.6
2.3
2.0
43.3
TiP_1:3
33.8
6.5
13.3
13.2
–21.5, −18.7
72.2
–3.8, −9.8
27.8
2.4
0.5
48.3
TiP_0:1
39.0
7.5
14.2
11.9
–9
100
2.3
0.0
56.6
Characterizations in
relation to formulae calculations. (a) TG curves (solid line and left y-axis) and DSC curves (dashed line and right y-axis). (b) 13C CP MAS NMR spectra. (c) 31P
MAS NMR spectra with peak deconvolutions. (d) Powder XRD patterns
of the calcined TiP materials compared with ICDD reference patterns.
(e) Raman spectra of the calcined TiP materials.To gain more insights into the composition
of the TiP materials, they were calcined at 800 °C under atmospheric
condition for 6 h. The resulting white powders were characterized
by SEM (Figure S1 in the Supporting Information), XRD, and Raman spectroscopy. The calcined TiP materials are composed
of titanium pyrophosphates (Figure d), including TiP2O7 and (TiO)2P2O7 (ICDD card numbers 00-038-1468
and 00-039-0207, respectively). The XRD peaks of these two pyrophosphates
overlap to some extent; nevertheless, we were able to distinguish
them using Raman spectroscopy. The peak at 720 cm–1 (Figure e) signifies
the presence of Ti–O–Ti chains that contain nonbridging
oxygen, as we discussed earlier. Therefore, only (TiO)2P2O7 can produce Raman scattering at 720 cm–1. A small amount of amorphous TiO2 is believed
to be present in all calcined samples because of the oxygen-rich calcination
environment. Amorphous TiO2 is a weak Raman scatterer and
thus cannot be fully characterized with this technique.[40]On the basis of all aforementioned characterizations,
we were able to determine the composition of the samples. The calculated
formulae are listed in Table . The detailed calculations and justifications are provided
as the Supporting Information. For the
TiP materials synthesized from mixed organic–inorganic precursors,
the inorganic-to-organic P ratios in the obtained materials are lower
than that in the synthesis liquor. Substantially higher Ti(IV) reactivity
was observed for HDBP than for H3PO4. The obtained
titanium(IV) butyl phosphate materials contain hydroxyl and oxy groups.
The increased oxy anion content from the TiP_1:0 to TiP_0:1 series
confirmed the results from Raman spectroscopy. Solvent extraction
of Ti(IV) by DEHPA yields the extractable [TiO(DEHPA)2]
complex, where deprotonated DEHPA acts as a bidentate ligand to occupy
the vacant coordination sites of the (TiO)2 chains.[41,42] The TiP_0:1 material is believed to have a similar structure (Scheme ).
Scheme 1
Proposed Structure
of the TiP_0:1 Material Showing the Layered Assembly and the Local
Coordination of Ti(IV)
Preliminary Investigation of Ln Uptake Capability
The
separation between early and late Ln3+ ions serves as a
reasonable indicator of the intralanthanide separation capability
of the TiP materials. Therefore, preliminary batch trials on competitive
Nd–Dy uptake were conducted. The Nd–Dy pair was chosen
also because of its industrial relevance with respect to the recycling
of NdFeB magnets. In all cases, the total Ln3+ uptake increased
with the elevated equilibrium pH (Figure S2a) and there were no significant differences in the total uptake amounts
between the TiP_0:1 and TiP_1:0 samples. However, the SF(Dy/Nd) values
for the TiP_1:0 sample stayed between 1 and 2 over the studied pH
range (1–3), whereas the same values for TiP_0:1 increased
with pH to more than 100 at approximately pH 2.8 (Figure S2b). In the hybrid TiP materials (TiP_1:3, TiP_1:1,
and TiP_3:1), the SF(Dy/Nd) maxima were observed in the pH range of
2.2–2.6. The increase of Nd3+ uptake after this
pH range was responsible for the subsequent decrease in SF(Dy/Nd).
The results of the preliminary investigation indicated that TiP_0:1
exhibited the best intralanthanide separation potential. Using the
purely inorganic TiP_1:0 as a comparison, the selective uptake of
the heavier Ln3+ by TiP_0:1 should originate from the effect
of the organophosphate functional groups. Therefore, the TiP_0:1 material,
prepared from a purely organophosphate precursor, was selected for
further separation and mechanism study in the current work. The hybrid
TiPs would find applications when the selectivity requirements are
not that high or when total Ln uptake is needed.
Proposed Ln3+ Uptake Mechanism and Kinetics
Ln3+ forms
nitrate complexes in aqueous solutions. TBP is a solvating organophosphate
extractant that coordinates to neutral Ln(NO)3 complexes
(eq ):Previously, we reported a group of
titanium(IV) alkyl-phosphate grafted silica materials that retain
Ln3+ in a solvating extraction manner.[21] The addition of nitrate salts significantly enhanced the
uptake of Nd3+ and Dy3+ on these grafted materials,
thereby suggesting that the uptake mechanism follows eq . However, the addition of 5 M NH4NO3 inhibited the Ln3+ uptake on the
TiP_0:1 material (Figure S3). To elucidate
the uptake mechanism, we closely monitored the Ln3+ uptake
kinetics in two sorption systems.The first proposed sorption
system I consisted of 2 mM Lu3+ at an initial pH of 1.8.
The uptake of Lu3+ appeared to be relatively slow, reaching
less than 30% of the equilibrium uptake after 24 h of mixing (Figure a). Notably, significant
amounts of Ti (soluble Ti(IV) ions irrespective of speciation) were
dissolved into the solution during the first 24 h. The shape of the
Ti dissolution amount curve in Figure a resembles that of the solution pH changes in Figure b. The Lu3+ uptake could, therefore, result from the transmetalation reaction:
metal cation exchange with framework TiO2+, according to eq . Here, the barred ions
refer to the solid phase.
Figure 3
Lu3+ uptake kinetics on the TiP_0:1 material (2 mM Lu3+).
Effect of contact time on (a) Lu3+ uptake and Ti dissolution,
(b) solution pH, and (c) n(Ti)/n(Lu3+) ratio.
Lu3+ uptake kinetics on the TiP_0:1 material (2 mM Lu3+).
Effect of contact time on (a) Lu3+ uptake and Ti dissolution,
(b) solution pH, and (c) n(Ti)/n(Lu3+) ratio.The ratio of dissolved Ti to Lu3+ uptake [n(Ti)/n(Lu3+)] was calculated
and is presented in Figure c. The n(Ti)/n(Lu3+) values are always below the theoretical value at 1.5 (according
to eq ) because of the
rapid precipitation reaction of TiO2+ (eq ), leading to the decrease in the
amount of dissolved Ti, the solution pH, and the n(Ti)/n(Lu3+) value.The second proposed sorption system II involved competitive
Nd3+ and Dy3+ uptake at an initial pH of 3.6.
Over the course of 20 d, the uptake of Nd3+ remained negligible
(<1 mg g–1) while more than 97% of Dy3+ was removed from the solution (Figure a). Although the dissolved Ti concentrations
were consistently lower than the detection limit (<10 μg
L–1), the drastic drop in the solution pH through
the initial 10 h of contact (Figure b) indicated the ion-exchange dissolution and rapid
hydrolysis of TiO2+ (faster reaction rate for eq at higher pH). The calculated SFs
[SF(Dy/Nd)] reached over 103 after 24 h.
Figure 4
Competitive Nd3+ and Dy3+ uptake kinetics on the TiP_0:1 material (1 mM
equimolar mixture of Nd3+ and Dy3+). Effect
of contact time on (a) Nd3+ and Dy3+ uptake,
(b) solution pH, and (c) SF(Dy/Nd).
Competitive Nd3+ and Dy3+ uptake kinetics on the TiP_0:1 material (1 mM
equimolar mixture of Nd3+ and Dy3+). Effect
of contact time on (a) Nd3+ and Dy3+ uptake,
(b) solution pH, and (c) SF(Dy/Nd).The sorption systems I and II were described by common kinetic
models, and the detailed results are given in the Supporting Information (Figure S4). On the basis of the obtained
high correlation coefficients (R2 close
to 1) and the closeness of the modeled equilibrium uptakes compared
with the experimental values, both of the kinetics in systems I and
II seem to obey the pseudo-second-order model (Table S2). However, further model validation suggested that
the errors are not normally distributed and certain points have an
unreasonably higher level of influence with a Cook’s distance
close to 0.5 (Figure S5–S6). The
models especially failed to fit the uptake kinetics during the initial
24 h of contact (Figure S7). For system
I, the initial accumulation of Ti4+ in the solution inhibited
the equilibrium in eq from shifting to the right side. For system II, the initial rapid
drop in solution pH influenced the reaction rate in eq and the speciation of Dy3+ in solution.When the TiP_0:1 material was equilibrated in
0.1 M HNO3, a negligible amount of Ti was detected in the
solution, thereby excluding the dissolution–precipitation mechanism.
Ln3+ complexes with dialkylphosphoric acids were determined
to be in a polymeric arrangement, in which each Ln3+ center
is surrounded by six oxygen atoms from the ligand in a pseudo-octahedral
environment.[43] Given the above observations,
the Ln3+ uptake on the TiP_0:1 sample is illustrated in Scheme . The selectivity
arises from the preferential transmetalation reaction (framework cation
exchange). Tasaki-Handa has systematically studied the Ln3+/Ln3+ ion-exchange behavior in the coordination polymers
based on DEHPA.[44,45] The ion-exchange affinity was
ascribed to coordination preference and steric strain. On the one
hand, because of the Ln contraction, the coordination preference follows
the reverse atomic number sequence in the Ln series. Smaller ions
coordinate stronger with the DBP groups. On the other hand, the steric
strain effect amplifies the same selectivity order. The ionic radius
of Ti4+ (74.5 pm) is significantly smaller than that of
Ln3+ (86.1–103.2 pm, six-coordinated). The non-isostructural
insertion of larger Ln3+ ions into the TiP framework requires
more energy because of the higher degree of structural distortion.
The level of steric strain caused by the TiO2+ ↔
Ln3+ exchange is expected to be even higher compared to
that by the equivalent Ln3+ ↔ Ln3+ exchange.
Thus, we were able to obtain higher SF(Dy/Nd) values compared with
earlier studies using equivalent framework ion exchange[46] and fraction precipitation by organophosphoric
acids.[10,26,27]
Scheme 2
Proposed
Transmetalation Reaction on the TiP_0:1 Material Demonstrating the
Exchange of Framework TiO2+ with Dy3+
To support the proposed mechanism,
the Dy3+-loaded TiP_0:1 material (after equilibrating for
20 d in system II, denoted as TiP_0:1_Dy) was characterized and compared
with pristine TiP_0:1 as well as the synthesized pure Dy(DBP)3 and/or Nd(DBP)3 coordination polymers. Powder
XRD patterns (Figure a) reveal the shrinkage of interlayer distance after Dy3+ exchange and structural distortion. Two peaks appeared for the TiP_0:1_Dy
sample corresponding to d spacings of 1.40 and 1.31
nm. Dy(DBP)3 crystallizes in a monoclinic fashion,[26] and the peak (d = 1.29 nm)
here represents the distance between the chains. The ATR–FTIR
spectra (Figure b)
show a doublet at approximately 1170 and 1100 cm–1, supposedly because of the vibration of the POO– group.[44] This exact doublet shifted toward
the value of Dy(DBP)3 in the TiP_0:1_Dy sample. The Raman
and UV–vis diffuse reflectance spectra were also checked before
and after Dy3+ loading, yet no evident changes were found.
Hydrolysis induced small amounts of −H2PO4 groups, as they were found by the 31P NMR peaks with
chemical shifts at −18.4 and −21.4 ppm in the TiP_0:1_Dy
material (Figure c).
Further studies in exploring the local coordination environment of
the loaded Ln3+ are needed to fully justify our proposed
mechanism.
Figure 5
Characterizations of Dy3+-loaded TiP_0:1 (TiP_0:1_Dy)
compared with the original TiP_0:1 and/or synthesized Dy(DBP)3 and Nd(DBP)3. (a) Powder XRD patterns in the 2θ
range of 5.0–7.5°. (b) ATR–FTIR spectra in the
900–1300 cm–1 range. (c) Solid-state 31P MAS NMR spectrum with peak deconvolutions.
Characterizations of Dy3+-loaded TiP_0:1 (TiP_0:1_Dy)
compared with the original TiP_0:1 and/or synthesized Dy(DBP)3 and Nd(DBP)3. (a) Powder XRD patterns in the 2θ
range of 5.0–7.5°. (b) ATR–FTIR spectra in the
900–1300 cm–1 range. (c) Solid-state 31P MAS NMR spectrum with peak deconvolutions.
Extraction from Dilute Ln3+ Mixtures
The ion-exchange uptake preference of Ln3+ on the TiP_0:1
material was tested under batch condition in a mixture consisting
of 10 mg L–1 of all Ln3+ ions. Because
of their chemical similarity, Sc3+ and Y3+ were
also added to the mixture. The extraction appeared to be pH-dependent,
and the increase of equilibrium pH increased the uptake (Figure a). The pH dependency
can be explained by eqs and 6. Sc3+, having the smallest
ionic radius, was completely retained by the material even at pHs
as low as 2.0. The extraction efficiency and Kd value for Y3+ lay between those for Ho3+ and Er3+, and this is concurrent with their ionic radii
for six-coordinated ions: 90.1 pm for Ho3+, 90.0 pm for
Y3+, and 89.0 pm for Er3+.
Figure 6
Extraction rates (a)
and distribution coefficients (Kd) values
(b) for metal uptake on the TiP_0:1 material. The ionic radii of the
tested elements with different coordination numbers are indicated
in (c).[3] Initial solution composition:
10 mg L–1 mixture of all Ln3+ (except
radioactive Pm3+) together with Sc3+ and Y3+. The maximum Kd value in the
study is presented as 199 800 mL g–1, calculated
from the detection limit (10 μg L–1).
Extraction rates (a)
and distribution coefficients (Kd) values
(b) for metal uptake on the TiP_0:1 material. The ionic radii of the
tested elements with different coordination numbers are indicated
in (c).[3] Initial solution composition:
10 mg L–1 mixture of all Ln3+ (except
radioactive Pm3+) together with Sc3+ and Y3+. The maximum Kd value in the
study is presented as 199 800 mL g–1, calculated
from the detection limit (10 μg L–1).Across the Ln series, the extraction
rate did not follow Ln contraction completely. Instead, the Ln “tetrad
effect” was observed.[47] The extraction
rate showed discontinuities at the positions of 1/4 filling (between
Nd and Pm) and half filling (Gd) of the 4f electron subshell. The
discontinuity at 3/4 filling (between Ho and Er) was not visible because
of high extraction rates. This effect is commonly observed in the
distribution of Ln in seawater and minerals, and it originates from
the variations of interelectronic repulsion for the ground states
across the Ln series.[48] In terms of the
distribution coefficients (Kd, Figure b), a clear dividing
line can be drawn between Gd and Tb. The present study establishes
that the group separation between early Ln (La–Gd) and late
Ln (Tb–Lu) could be effectively carried out on the TiP materials.
The group SFs [SF(Tb–Lu/La–Gd)] were calculated as 2.0
± 0.3, 28.7 ± 0.4, 203.1 ± 3.4, and 112.5 ± 35.3
at, respectively, pH 2.0, 2.6, 3.2, and 4.2.
Binary Ln3+ Separation
Models
Binary Ln3+ uptake experiments were carried
out to investigate in detail the potential separation behavior. Seven
combinations were chosen across the Ln series: La–Ce, Pr–Nd,
Eu–Gd, Gd–Tb, Tb–Dy, Yb–Lu, and Nd–Dy.
The uptake of Ln3+ by the TiP_0:1 material from the 1 mM
equimolar binary mixture was monitored as a function of solution equilibrium
pH. Among these combinations, the first six represent adjacent Ln
pairs, whereas the last one is a typical example for early and late
Ln separation. The adjacent Ln pair Gd–Tb was studied because
their distribution coefficients signify a clear discontinuity in the
earlier section.Adjacent Ln pairs are known to share extremely
similar chemical properties, and their separation is one of the most
difficult tasks in inorganic separations. The similarities of the
adjacent Ln pairs are observed based on the almost identical shape
of their Kd versus pHeq curves
(in Figures S8–S13, Supporting Information). The uptake preference (represented by the SFs, Figure a–f) in the current
case strictly followed the reversed Ln contraction order (Lu3+ → La3+), whereby Ln3+ ions with smaller
radii were preferentially retained. This deviates from the Ln tetrad
effect. We suggest that the tetrad effect only becomes evident if
the concentrations of Ln are relatively low. If there are large amounts
of competing Ln3+ ions, the coordination and steric strain
preferences favor the smaller Ln3+. The separation between
Gd and Tb is significantly easier compared to that between Eu and
Gd, although both pairs are adjacent Ln. These results confirm the
group separation behavior that Ln series is divided into two subgroups:
from La to Gd as early Ln and from Tb to Lu as late Ln in our current
work. In addition, significant Nd–Dy separation was achieved
(Figures g and S14),
possibly because of their larger differences in ionic radii.
Figure 7
SFs between
selected Ln3+ pairs [(a) La–Ce; (b) Pr–Nd;
(c) Eu–Gd; (d) Gd–Tb; (e) Tb–Dy; (f) Yb–Lu;
and (g) Nd–Dy] as a function of solution pH. Initial solution
composition: 1 mM equimolar mixture of the selected Ln3+ pair. The corresponding Kd values are
available in Figure S8–S14 in the Supporting Information.
SFs between
selected Ln3+ pairs [(a) La–Ce; (b) Pr–Nd;
(c) Eu–Gd; (d) Gd–Tb; (e) Tb–Dy; (f) Yb–Lu;
and (g) Nd–Dy] as a function of solution pH. Initial solution
composition: 1 mM equimolar mixture of the selected Ln3+ pair. The corresponding Kd values are
available in Figure S8–S14 in the Supporting Information.The sole external parameter
contributing to the separations is the equilibrium pH of the solution
in our proposed system. This means that, through delicate control
over the solution pH, optimal separations can be achieved either by
leaving the majority of the larger Ln3+ in the solution
or by exchanging the majority of the smaller Ln3+ onto
the TiP material. The optimal molar fractions (best values obtained
from the binary competitive batch systems) of the Ln in the liquid
and solid phases are plotted in Figure a. Through only one uptake cycle, the heavier Ln in
the adjacent Ln pairs was concentrated in the solid phase, representing
some 60–80% of the total Ln fraction. Concurrently, the lighter
Ln was concentrated in the liquid phase. The separation of Nd and
Pr remained the most difficult one. Notably, almost complete Nd–Dy
separation was achieved batchwise, as more than 99% of the loaded
Ln was Dy.
Figure 8
(a) Stacked column plots showing the optimal Ln fractions in the
solid and the liquid phases obtained from the binary uptake study
at different equilibrium pH values. (b) Dependence of the best achieved
SFs using a logarithmic scale on the ionic radii difference of the
Ln3+ pairs.
(a) Stacked column plots showing the optimal Ln fractions in the
solid and the liquid phases obtained from the binary uptake study
at different equilibrium pH values. (b) Dependence of the best achieved
SFs using a logarithmic scale on the ionic radii difference of the
Ln3+ pairs.Because the separation capability originates from the small
differences in ionic radii, we plotted the best achieved SFs (on a
logarithmic scale) versus the differences in ionic radii (Figure b). Ln3+ forms an Ln(DBP)3 complex; therefore, the ionic radii
of six-coordinated ions were used. The linear regression line was
drawn, and it appears that a larger difference in the ionic radii
is positively correlated with the separation behavior. Overall, these
results emphasize the potential technological significance of the
TiP materials in Ln separation.
Transmetalation as a Metal
Separation Process
Transmetalation is a type of organometallic
reaction during which the organic ligands are transferred from one
metal ion to another. It has been shown in recent years that MOFs
and coordination polymers are applicable hosts for transmetalation.
Partial, core–shell, complete, or even single-crystal-to-single-crystal
metal exchanges were reported.[49] The metal
exchange depends on ionic radii differences, preferential coordination
geometries, kinetics, framework flexibility, and solvent effects.[50] It appears that transmetalation on water-stable
MOFs and coordination polymers is worth exploring as a hydrometallurgical
metal separation approach. The effects of codissolving metal ions
(Fe3+, Al3+, Ca2+, etc.) in real
samples need to be taken into consideration when further assessing
the performance of the process. However, the intralanthanide separation
is still preferably to be placed as a downstream process when all
other metal ions, except for Ln3+, are eliminated.
Comparison
with Literature Results
Table summarizes some intralanthanide separation approaches
reported in recent years, with an emphasis on solvent extraction,[51] solvent leaching,[52] crystallization,[8,15,26] and ion-exchange methods.[25,46] Organic phosphorus-containing
ligands are in general selective for Ln separation. Our method appears
to be the best in terms of SF, though this is far from the sole judgmental
factor for a successful separation process. Titanium(IV) serves as
sacrificial ion-exchange sites, and the dissolved TiO2+ hydrolyzes into hydroxides. In reality, the complete regeneration
of the material might not be possible because of the formation of
titanate phases. Additionally, organophosphates can be attacked by
H+, hydrolyzing into inorganic phosphate and alcohol. Finding
a reasonable compromising point between selectivity and operational
ease marks out our road ahead. The ultimate goal is a solvent-free,
efficient, recyclable, and selective method that requires neither
toxic chemicals nor intensive energy input.
Table 4
Intralanthanide
Separation Capability Comparisons with Literature Reported Approaches
classification
method/reagent
target
Ln pair
SF
references
solvent extraction
DEHPA
Nd–Dy
12.93
(51)
Cyanex 923
Nd–Dy
12.79
(51)
solvent
leaching
tripodal
nitroxide ligand
Nd–Dy
359
(52)
crystallization
HDBP
Nd–Dy
>300
(26)
borate
Nd–Dy
986
(8)
camphorate
Tb–Dy
1.247
(15)
ion exchange
amorphous zirconium phosphate
Nd–Dy
1.9
(25)
Ce(DEHP)3
La–Dy
1.6
(46)
Fe(DEHP)3
La–Dy
18.4
(46)
Al(DEHP)3
La–Dy
3.5
(46)
titanium(IV)butyl phosphate
Nd–Dy
2065
this work
Tb–Dy
11.5
this work
Conclusions
We have demonstrated the basis of a Ln separation strategy utilizing
a transmetalation reaction on layered titanium(IV) organophosphate
materials, as opposed to the extraframework ion-exchange materials.
These coordination polymers were easily prepared by a precipitation
reaction and showed potential in intralanthanide separation, especially
for the separation between early and late Ln. The selective Ln uptake
was controlled by solution pH and did not require any additional energy
input (e.g., hydrothermal condition). The selectivity arose from the
ligand coordination and steric strain preferences during the transmetalation
reaction and structural distortion. The separation performance of
the transmetalation reaction seems higher compared to the selective
crystallization or solvent extraction process utilizing the same or
a similar organophosphate ligand. That said, the stability of the
material as well as the regeneration needs to be further studied to
warrant the design of a true separation process. Through alterations
of the framework metal (size and valence) and organophosphate ligand,
a variety of new MOF or coordination polymer materials can be envisioned
with enhanced and tunable metal selectivity in aqueous solutions.