Adsorption Properties of Sepiolite in Relation to Uranium and Lanthanide Ions

: The batch technique was used to study the adsorption of La(III), Eu(III), Lu(III), and U(VI) ions on sepiolite and ODTMA–sepiolite under ambient conditions. The e ﬀ ects of pH, time, and initial concentration were investigated. The highest U(VI) adsorption was found on ODTMA-sepiolite in the pH range of 6–8, while in the case of lanthanide ions, adsorption on sepiolite was 80% in the pH range of 4–8 and 98% for pH values above 8. The adsorption capacity of ODTMA-sepiolite was found to be 285.6 mg / g for uranium, and raw sepiolite: 142.8 mg / g for U(VI), 91.6 mg / g for La(III), 91.4 mg / g for Eu (III), and 104.9 mol / g for Lu(III). ODTMA–sepiolite turned out to be a weak sorbent for lanthanide ions. Two short- and long-lived ﬂuorescence species were observed in the TRLFS spectra of U(VI) adsorbed on sepiolite at pH 6.5. The average lifetimes of short- ( τ 1) and long-lived ( τ 2) ﬂuorescence are τ 1 = 2420 ± 430 ns and τ 2 = 37950 ± 5710 ns for U-sepiolite; τ 1 = 3523 ± 160 ns and τ 2 = 45400 ± 1830 ns for U-ODTMA–sepiolite.


Introduction
Uranium, an actinide element, is of significant importance in the fuel cycle, beginning as a source and ending up as the final waste component. Anthropological sources of U contamination fall into three categories: originating from weapon production, nuclear energy, and various other uses [1]. Uranium occurs in both seawater and a large number of rocks with 2 to 4 parts per million concentrations in the Earth's crust. UO 2 2+ is the main form of released uranium in the environment. A major environmental problem, however, is its contamination (radioactivity and toxicity). The methods of uranium(VI) ions removal-adsorption, solvent extraction, or ion exchange for U(VI) purification from waste waters-have been recently elaborated upon. Currently, adsorption based on metal oxides [2]-activated carbon [3] aluminosilicates [4][5][6] as adsorbents-is the most common method of uranium removal in aquatic environments. Zeolites, wood powder, clay, and chitosan, which are natural products, as well as those of microbiological biomass, are regarded as affordable adsorbents because of their low price and accessibility [7]. Hence, researchers have been focusing on effective natural adsorbents. This paper discusses U(VI) and the three lanthanide ions' (La, Eu, Lu) adsorption on sepiolite, a natural adsorbent. Lanthanides are regarded as chemical analogs of actinides; thus, it is interesting to compare the adsorption capacity of sepiolite in relation to such ions. The presence of lanthanides in our environment is associated with their ever-increasing importance in everyday life-applications in fiber optic lasers, as ionic conductive oxides, or in microelectronics as oxides. They can also be used as liquid crystals or surfactants. Thus, there is a great demand for increased mining of ores containing lanthanides, propelling the mobility of rare earth elements (REE) and subsequently resulting in a higher REE content in various organisms [8]. It is commonly believed that lanthanides do not play a great role in physiological reactions in living organisms. Although they are not known to be necessary for metabolic processes, they can have a positive effect under certain conditions. As follows from recent toxicological investigations on chlorides of rare elements, the toxicity of lanthanides is similar to that of CdCl 2 [7][8][9][10].
The main objectives of this paper were to investigate and compare uranium ions and the sorption of three lanthanides on natural sepiolite with the formula (Si 12 )Mg 8 O 30 (OH) 6 (OH 2 ) 4 ·8H 2 O [10] or on the modified ODTMA (octadecyltrimethylammonium bromide). We took into account the fact that reports of sorption of U(VI) are scare in the literature in comparison to that of lanthanide ions. To supplement the description and effectiveness of the adsorption system, adsorption at pH, in time, and at the initial concentration of adsorbent ions function was investigated. We used two types of adsorbents: natural and modified with organic salt (organoclays have a greater affinity for uranyl ions [11][12][13][14][15][16]). The structure of clay changes from hydrophilic to hydrophobic with the incorporation of large organic cations. Thus, organoclay, being a hybrid material, is able to adsorb inorganic and organic impurities (such as aliphatic or aromatic hydrocarbons [17]) as anions such as I − , Cl − , phospate(V) with cations, i.e., Pb 2+ , Hg 2+ , UO 2 2+ found in nuclear waste [18].

Materials
Sepiolite was delivered by Anadolu Endüstri Mineralleri (Turkey). Its chemical composition is presented in Table 1. The natural sepiolite was treated with octadecyltrimethylammonium bromide (ODTMA-Br), C 21 H 46 N·Br, FW: 392.52 (Sigma-Aldrich, Steinheim, Germany) in order to intensify adsorption. Organoclay was prepared as follows: 100 cm 3 of 1 or 5 mmol/dm 3 ODTMA-Br solution was mixed with 1 g of sepiolite at 60 • C for 4 h. The sepiolite was then removed from the solution via filtration, washed twice with distilled water, dried in air, and after powdering in the agate mortar was passed through a 0.1 mm sieve. This sepiolite was designated as ODTMA-sep.

Sorption Determination
Adsorption was studied by means of the batch method at 23 • C. Mixtures (100 cm 3 ) were prepared with 0.1 g of adsorbent and UO 2 (COOCH 3 ) 2 ·2H 2 O solution or Ln(NO 3 ) 3 (Ln = La, Eu or Lu) with the desired concentration of ions. They were then shaken for 6 h, filtered using filter paper (Filtrak 390), and centrifuged at 10,000 rpm for 10 min. The amount of U(VI) or Ln(III) ions adsorbed on sepiolite was determined based on the difference between the initial and equilibrium concentrations using the following equation: where c ads , c in , c eq are the concentrations of Ln(III) or U(VI) ions in the clay phase, in the initial and equilibrium solutions, respectively; A% means the adsorption percentage in the aqueous solution.
V and m indicate solution volume (cm 3 ) and adsorbent mass (mg). The concentrations of U(VI) and lanthanides were determined by the Arsenazo III method [19]. To this end, uranium solutions or a corresponding lanthanide with the addition of 0.05% Arsenazo(III), formic buffor of pH 2.6 as well as 1% ascorbic acid, was used. The absorbance of these solutions was measured by means of spectrophotometer Jasco 660 at wavelengths 650 nm and 655 nm for lanthanides and uranium ions, respectively. Kinetic experiments and study of the pH value effect were conducted at an initial concentration of 0.5 mmol/dm 3 . The PH effect from uranium or lanthanide ions' adsorption was in the pH range 2-11. HNO 3 or NaOH solution was added to adjust the pH value. All experimental data were averaged with triplicate determinations. Data errors were about 5%.

Methods
Sorbent surface morphology was observed using a scanning electron microscope, Quanta 3D FEG, FEI Company, Hillsboro, OR, USA.
Clay spectra were recorded using the Nicolet 8700A FT-IR spectrometer (Thermo Scientific, Waltham, MA, USA, 2009), with TGS detector of 1 cm −1 resolution in transmission mode at room temperature. The KBr pellet technique (1:20) was applied. After drying at 200 • C for 24 h, 560 mg KBr was homogenized with sepiolite in a ball grinder (Narva, Brand-Erbisdorf, Germany). Tablets with 1 cm radius and thickness of 0.1 cm were prepared by means of a hydraulic press. Nitrogen adsorption was measured at 77 K by volumetric analyzer AUTOSORB-1CMS (Quantachrome Instruments, Boynton Beach, FL, USA, 2005). Before measurements, each sample was degassed at 100 • C for minimum 6 h to obtain 10 −3 hPa. XRD analysis was performed by means of a diffractometer equipped with a Rtg generator of the ISO-DEBYFLEX 303-60 kV type, produced by Seifert Analytical X-ray (Middle Watch, Swavesey, UK), and a cooling system KMW 3000C from Rigaku Oxford Diffraction (Abingdon, UK). The measurement data were collected, analyzed, and processed using the XRAYAN program (version 4.2.2, KOMA, Warsaw, Poland).
An ESCA apparatus with multidetection electron analyzer Scienta R4000 (VG Scienta) (CEO Scienta Omicron Company GmbH, Taunusstein, Germany) was used to record XPS spectra in the fixed transmission mode. An unmonochromatized Al Kα source (1,253.6 eV) with 12 kV voltage and 30 mA emission current was also employed. After powdering, the samples were kept in a molybdenum holder in 5 × 10 −8 mbar vacuum. The CASA XPS software (version 2.3.22, Shimadzu Group Company, Tokyo, Japan) with a Gaussian-Lorentzian peak shape was used for U 4f spectra fitting after background subtraction with a Shirley baseline. The uranium 4f spin-orbit coupling was at 10.8 Ev.
Sepiolite luminescence was registered at room temperature with a Photon Technology International fluorescence spectrophotometer using the Nd:YAG diode laser (Opolette, Quantel, Carlsbad, CA, USA).
The materials for the XPS, SEM, FTIR, and fluorescence measurements were obtained by mixing 2 g of the ODTMA-sep or sepiolite with 100 cm 3 of UO 2 (CH 3 COO) 2 or Ln(NO 3 ) 3 solution (0.01 mol/dm 3 ) for 8 h. They were then separated by filtration, followed by drying in air.

Surface Propetries of the Sepiolite
A comparison of sepiolite before and after ion adsorption concludes that there is a significant decrease in the surface area of micropores and volume, total pore volume, and BET surface area during clay modification using the ODTMA-Br solution. This is a consequence of the clogging of micropores by large cations of alkylammonium salt; only mesopores remain accessible ( Table 2). The average pore diameter increases as a result of reduction in the number of small pores, as well as the formation of secondary pores derived from collapsed surfactant alkyl chains. Such changes are typical of the adsorption of large organic ions [20][21][22][23][24][25]. After uranium adsorption, the values of total pore volume and average pore diameter diminished, which was attributed to the adsorption of uranium ions: UO 2 2+ or/and hydroxycomplexes: (UO 2 )(OH) + , (UO 2 ) 3 (OH) 5 + . In the case of sepiolite samples saturated with lanthanide ions La, Eu, and Lu, a significantly smaller surface reduction was observed than in the case of the sepiolite U-1mM-ODTMA or sepiolite samples 1mM-, 5mM-ODTMA. This can be explained by the smaller sizes of Ln 3+ (about 1 Å) or Ln-O (less than 2.64 Å) [26] compared to uranium ions that can reach 6 Å, depending on the type of coordination sphere. Large and smaller pores are occupied by In each case, the BET surface is also reduced, as a result of ion adsorption.

Scanning Electron Microscopy Analysis
The surface of sepiolite modified by the surfactant and uranium is smoother and flat, when compared to that of the natural adsorbent ( Figure 1). This is probably due to the layers of organic matter partially covering the sepiolite surface. Additionally, single and small grains are visible on the surface, which may be due to uranyl hydroxy carbonate or/and hydroxide as a new phase. In the XRD spectrum of U-1mM_ODTMA-sepiolite, apart from characteristic peaks for sepiolite, weak peaks derived from uranyl carbonate were also found. In addition, weak peaks of lanthanide carbonates occurred in samples of sepiolite modified with the appropriate lanthanide ( Figure 2). and smaller pores are occupied by small ions Ln 3+ or Ln(OH)2 + , Ln(OH) 2+ , LnCO3 + , and LnHCO3 2+ and Ln(NO3) + ; and therefore, the average pore size remains smaller than that of the ODTMA sepiolite and U-ODTMA sepiolite samples. In each case, the BET surface is also reduced, as a result of ion adsorption.

Scanning Electron Microscopy Analysis
The surface of sepiolite modified by the surfactant and uranium is smoother and flat, when compared to that of the natural adsorbent ( Figure 1). This is probably due to the layers of organic matter partially covering the sepiolite surface. Additionally, single and small grains are visible on the surface, which may be due to uranyl hydroxy carbonate or/and hydroxide as a new phase. In the XRD spectrum of U-1mM_ODTMA-sepiolite, apart from characteristic peaks for sepiolite, weak peaks derived from uranyl carbonate were also found. In addition, weak peaks of lanthanide carbonates occurred in samples of sepiolite modified with the appropriate lanthanide ( Figure 2).
The band at 441-440 cm −1 originates from the octahedral-tetrahedral bonds (Si-O-Mg bonds) and the bands at 650-648 cm −1 correspond to vibrations of the Mg-OH bond [26,27]. The bands at 690 cm −1 are assigned to the Si-O bonds deformation and bending modes [28]. Adsorbed water affects the H-O-H (1600-1700 cm −1 ) and O-H stretching (3200-3700 cm −1 ) regions. The band position is gradually shifted from 1663 cm −1 to 1659 cm −1 with increasing concentrations of the surfactant. At the same time, a remarkable decrease of absorption intensity was observed, pointing to a smaller number of hydrogen-bound H 2 O molecules in the organoclay; this is characterized by a higher surfactant concentration, possibly caused by the reduction of H 2 O content due to its replacement by ODTMA + . As a result of surfactant intercalation, sepiolite surface properties are modified-hydrophilic to hydrophobic. At the same time, U(VI) ions' adsorption on the sepiolite surface contributes to this band intensity increase, which is related to strong hydration of uranyl ions. A similar case is observed for those in the 3200-3420 cm −1 area, associated with the stretching vibrations of structural OH groups and adsorbed water. These bands show little dependence on surfactant concentration. A slight shift of the bands towards higher wavenumbers is observed with a decrease in water content in the ODTMA-sep. Their intensity growth decreases with increasing surfactant concentration after U(VI) ions' adsorption. At 2855 and 2928 cm −1 bands, they are equal to symmetric and asymmetric stretching modes of CH2 groups derived from the surfactant, i.e., ODTMA. Their intensity grows gradually with increasing ODTMA concentration, resulting in the rise of amine chains packing density in sepiolite galleries. Tensile frequencies of CH2 groups are sensitive to conformational changes and depend on amine concentration. At high ODTMA concentration, the chains remain ordered (all-trans conformation), and in the FTIR spectrum, there are narrow absorption bands with relatively constant frequency. At low concentrations of the surfactant, Gauche conformers are present, resulting in the frequency shifting towards the high waves. In the case of ODTMA-sep, the wavenumbers of absorption bands (symmetric and asymmetric CH2 stretching) change from 2856 to 2855 cm −1 and 2928 to 2930 cm −1 , respectively. In the case of ODTMA-sep, the wavenumbers of absorption bands (symmetric and asymmetric stretching of CH2) are virtually unchanged and amount to 2855 cm −1 (1mM_ODTMA-, 5mM_ODTMA-sepiolite), 2856 cm −1 ((U-1mM_ODTMA)-sepiolite); and 2928, 2929, 2930 cm −1 , respectively. The band between 1463 and 1459 cm −1 may be linked with C-O-H or C-H groups vibrations [27]. Its frequency is less sensitive to conformation of the amine chain; therefore, we do not observe a change in the position of this band with an increase in the ODTMA cation content in the sample. In the case of a sample of sepiolite with the adsorbed uranyl ions, the intensity of this band decreases and its position varies from 1463 to 1459 cm −1 . This may indicate interactions between the uranyl ions and the alkyl chains of the surfactant cation.    The kind of U(VI) surface complexes on sepiolite was investigated by applying the time-resolved laser-induced fluorescence spectroscopy (TRLFS). It obtained information on the lifetime of the adsorbed species and spectral characteristics indicating the number of species and their spectral identities. Information about fluorescence emission bands position and fluorescence lifetime can be obtained using uranium(VI) species TRLFS measurements. The number of U(VI) atoms surrounding the water molecules affects the fluorescence lifetime. As follows from the TRLFS spectra of U(VI) surface species adsorbed on sepiolite at pH 6.5, there are at least two surface species with different fluorescence lifetimes, namely: a short-lived one and a long-lived one. The average short-(τ 1 ) and long-lived (τ 2 ) species fluorescence lifetimes for U-sepiolite are: τ 1 = 2420 ± 430 ns and τ 2 = 37950 ± 5710 ns; for U-ODTMA-sepiolite: τ 1 = 3523 ± 160 ns and τ 2 = 45400 ± 1830 ns. Shorter fluorescence lifetimes indicate more water molecules in the coordination environment-it indicates a quenching by water molecules [29][30][31]. Thus, U(VI) forms two surface species on sepiolite, differing in the number of water molecules in the coordination environment. The comparison of fluorescence lifetimes with and without ODTMA shows remarkably longer fluorescence lifetimes of both species with ODTMA. Shorter U_ODTMA-sep fluorescence lifetimes point to a larger number of water molecules in the coordination environment of corresponding U(VI) surface species. According to Bauman et al. [30], surface species with shorter fluorescence lifetime can be a result of bidentate mononuclear inner-sphere surface complexes, where U(VI) is bound to reactive hydroxyl groups at the broken edge connected with an Al molecule. Surface species with shorter fluorescence lifetime were assigned by Arnold et al. [7] to the inner-sphere bidentate surface complex, where U(VI) is bound to the aluminol groups of muscovite edge-surfaces. According to both scientists, surface species with remarkably longer fluorescence lifetimes can be treated as an amorphous U(VI) condensate nanosized cluster of uranyl surface species.

X-ray Photoelectron Spectroscopy Analysis
Coexistence of the C, O, Mg, Si, and U bands is illustrated by survey spectra presented in Figure 4a. Four individual peaks at 284.7, 286.3, 287.9, and 290.0 eV, which are assigned to C-C, C-O, C=C, and O=C-O, respectively, make the spectrum of C1s [32]. Two peaks, the highest at 532. 6  as well as that of non-stoichiometric uranium (VI) oxides [33].

Equilibrium Data of Sorption on Sepiolite
In order to describe the adsorption behavior of uranium and lanthanides on sepiolite, the Langmuir, Langmuir-Freundlich, and Dubinin-Radushkevich adsorption models were used to fit the obtained isotherms. The Langmuir behaviour was tested by the following equation in a linearized form: The following is the expression for the Langmuir-Freundlich isotherm: The apparent adsorption energy was estimated using the Dubinin-Radushkevich isotherm. Its linear form is as follows: where, cs and ceq are the equilibrium concentrations of U(VI) in the clay (mol/g) and aqueous phases (mol/dm 3 ), amax, qm, K, n-the adsorption maximum, maximum capacity, adsorption constant, heterogeneity parameter of the surface, respectively. R denotes the gas constant (8.314 J/mol K), T represents the absolute temperature (K). The parameter values calculated based on the intercept slopes of the plots are included in Table 5. Adsorption apparent energy (E) can be determined from:

Equilibrium Data of Sorption on Sepiolite
In order to describe the adsorption behavior of uranium and lanthanides on sepiolite, the Langmuir, Langmuir-Freundlich, and Dubinin-Radushkevich adsorption models were used to fit the obtained isotherms. The Langmuir behaviour was tested by the following equation in a linearized form: The following is the expression for the Langmuir-Freundlich isotherm: The apparent adsorption energy was estimated using the Dubinin-Radushkevich isotherm. Its linear form is as follows: where, c s and c eq are the equilibrium concentrations of U(VI) in the clay (mol/g) and aqueous phases (mol/dm 3 ), a max , q m , K, n-the adsorption maximum, maximum capacity, adsorption constant, heterogeneity parameter of the surface, respectively. R denotes the gas constant (8.314 J/mol K), T represents the absolute temperature (K). The parameter values calculated based on the intercept slopes of the plots are included in Table 5. Adsorption apparent energy (E) can be determined from: The adsorption isotherm of uranium ions on ODTMA-sep shows an increasing tendency (Figure 5a). The rapid increase in adsorption is observed for concentrations higher than 0.11 mmol/dm 3 . As expected, the uranyl ions' adsorption on ODTMA-sep is much higher than that on natural sepiolite for the studied initial concentration range. Studies on the parameters of isotherms and coefficients of correlation (R 2 ) ( Table 5) show that the Langmuir-Freundlich model is the best for description of U(VI) adsorption on natural sepiolite (R 2 = 0.98) and ODTMA-sep (R 2 = 0.97). The parameter value of n < 1 points to the significant heterogeneity of the sorbent surface. The energy value calculated on the basis of the Dubinin-Radushkevich isotherm equation (E = 14.5 and 13.3 kJ/mol) indicates that chemisorption is the dominant mechanism.
Pseudosecond-order kinetics The adsorption isotherm of uranium ions on ODTMA-sep shows an increasing tendency ( Figure  5a). The rapid increase in adsorption is observed for concentrations higher than 0.11 mmol/dm 3 . As expected, the uranyl ions' adsorption on ODTMA-sep is much higher than that on natural sepiolite for the studied initial concentration range. Studies on the parameters of isotherms and coefficients of correlation (R 2 ) ( Table 5) show that the Langmuir-Freundlich model is the best for description of U(VI) adsorption on natural sepiolite (R 2 = 0.98) and ODTMA-sep (R 2 = 0.97). The parameter value of n < 1 points to the significant heterogeneity of the sorbent surface. The energy value calculated on the basis of the Dubinin-Radushkevich isotherm equation (E = 14.5 and 13.3 kJ/mol) indicates that chemisorption is the dominant mechanism. The adsorption of La 3+ , Eu 3+ , and Lu 3+ ions on natural sepiolite is in the range of 0.4-0.48 mmol/g and, as expected, much higher than on the modified form with ammonium salt, i.e., ODTMAsepiolite. Lanthanide adsorption isotherms show an upward trend and saturation of the adsorbent monolayer has not been reached the range of the tested concentrations (0.1-1 mmol/dm 3 ) (Figure 6a). The parameters from the isothermal modelling are presented in Table 5. The values of energy for individual lanthanide ions calculated from the Dubinin-Radushkevich equation are from E = 11.2 to The adsorption of La 3+ , Eu 3+ , and Lu 3+ ions on natural sepiolite is in the range of 0.4-0.48 mmol/g and, as expected, much higher than on the modified form with ammonium salt, i.e., ODTMA-sepiolite. Lanthanide adsorption isotherms show an upward trend and saturation of the adsorbent monolayer has not been reached the range of the tested concentrations (0.1-1 mmol/dm 3 ) (Figure 6a). The parameters from the isothermal modelling are presented in Table 5. The values of energy for individual lanthanide ions calculated from the Dubinin-Radushkevich equation are from E = 11.2 to E = 11.5 kJ/mol, which is characteristic of the chemical adsorption mechanism. In the case of lanthanide ions, ion exchange adsorption between Mg 2+ ions and Ln 3+ ions could possibly be a major process.
The increase of U(VI) adsorption on natural sepiolite was very quick at initial contact (Figure 5c). The maximum amount of adsorbed uranium was obtained after just 60 min. Then, 360 min after the start, desorption of uranium previously adsorbed by sepiolite was observed. An increase in uranium adsorption was found later. However, the amount of adsorbed ions was much smaller than in the first period of fast adsorption. A similar decrease in the case of adsorption of uranium on diatomite from 40 min to 90 min after the start was observed by Sprynskyy et al. [34]. The uranium desorption is explained by the authors based on the fact that exchangeable cations and diatomite surface hydrogen ions compete with the solution's uranium ions. The U(VI) adsorption on ODTMA-sepiolite was also fast for the first hour of contact time, then increased slowly with time. In this case, there was no decrease in adsorption with time progression. The fast U(VI) adsorption on ODTMA-sepiolite may indicate its dominance due to chemical adsorption through surface complexation but not physical adsorption. The analysis of the data of U(VI) adsorption on sepiolite was made by three kinetic models: the pseudo-first-order: the pseudo-second-order: The Weber-Morris intraparticle diffusion model expressed as: where q e and q t indicate the amounts of uranium ions adsorbed at equilibrium in mg/g, and at time t in min, respectively, and k 1 , k 2 and k 3 show the rate constants. The calculated parameters and correlation coefficients (R 2 ) values are presented in Table 5. For high correlation coefficient values, it can be deduced that the sorption system is based on the pseudo-second order kinetic model. The adsorption mechanism proceeds mainly by chemisorption (especially ion exchange), as adsorption follows the pseudo-second order model [35].
Minerals 2019, 9, x FOR PEER REVIEW 11 of 16 E = 11.5 kJ/mol, which is characteristic of the chemical adsorption mechanism. In the case of lanthanide ions, ion exchange adsorption between Mg 2+ ions and Ln 3+ ions could possibly be a major process. The increase of U(VI) adsorption on natural sepiolite was very quick at initial contact ( Figure  5c). The maximum amount of adsorbed uranium was obtained after just 60 min. Then, 360 min after the start, desorption of uranium previously adsorbed by sepiolite was observed. An increase in uranium adsorption was found later. However, the amount of adsorbed ions was much smaller than in the first period of fast adsorption. A similar decrease in the case of adsorption of uranium on diatomite from 40 min to 90 min after the start was observed by Sprynskyy et al. [34]. The uranium desorption is explained by the authors based on the fact that exchangeable cations and diatomite surface hydrogen ions compete with the solution's uranium ions. The U(VI) adsorption on ODTMAsepiolite was also fast for the first hour of contact time, then increased slowly with time. In this case, there was no decrease in adsorption with time progression. The fast U(VI) adsorption on ODTMAsepiolite may indicate its dominance due to chemical adsorption through surface complexation but not physical adsorption. The analysis of the data of U(VI) adsorption on sepiolite was made by three kinetic models: the pseudo-first-order: the pseudo-second-order: The Weber-Morris intraparticle diffusion model expressed as: Lanthanide ions' adsorption on natural sepiolite remains constant at around 80% after 3 h. The parameters of kinetic models used in calculations are presented in Table 5.
The effect of pH on ions adsorption on sepiolite is of importance. As follows from Figure 5b, uranyl ions' adsorption on both sorbents grows when the pH values increase at pH < 6, reaching the maximal value at pH 6-8; it then drops when the pH value increases. Uranium ions adsorption on clay follows the outer sphere or ion exchange complexation with low values of pH as well as that of inner sphere when the pH values are high. Furthermore, the increase of pH favors the formation of oligomeric uranium hydroxy complexes, especially (UO 2 )(OH) + , (UO 2 ) 3 (OH) 5 + and (UO 2 ) 4 (OH) 7 + species [36], which occupy more active adsorption sites on the mineral surface than simple UO 2 + cation.
The decrease of adsorption can be justified by various anionic uranium(VI) complexes present at different values of pH. According to Han et al. [37], at pH > 6, the amount of dissolved anion complexes with U(VI) grows, resulting in decreasing U(VI) adsorption on unmodified sepiolite. In the case of ODTMA-sep, the U(VI) adsorption decrease at higher values of pH is negligible due to interactions of anionic complexes with a positively charged mineral surface. The adsorption of lanthanide ions increases with the increasing pH and is established at a constant level of about 80% for the pH range of 4-8 (Figure 6b,e). In this area of pH, the exchange between the H + ions coming from the silanol group contained in the sepiolite structure and lanthanide ones occurring in the form of Ln 3+ ions or hydroxycomplexes Ln(OH) 2+ and Ln(OH) 2 + is most likely a chemisorption reaction. Further increase in pH leads to an increase in adsorption to 98%, which is probably due to the precipitation of lanthanide hydroxides Ln(OH) 3 at pH above 8. This fact leads to a decrease in their concentration in equilibrium solutions and, as a result, an increase in the percentage of lanthanide adsorption on sepiolite is observed. Such precipitated hydroxides or carbonates settle down on the sepiolite surface or are partially complexed by it. It is evident from Figure 6d,e that the adsorption of lanthanide ions on ODTMA-sepiolite is much lower. This is due to the presence of ODTMA + ions on the sepiolite surface, which makes it positively charged and thus prevents interactions with Ln 3+ cations. In addition, the large ODTMA + ions clog up the sepiolite pores and make access to the lanthanide cations difficult.

Proposed Mechanism of Adsorption
Based on the FTIR, XPS analysis, and batch studies, the probable adsorption mechanism of lanthanides and uranium(VI) ions on sepiolite can be suggested. One of the possible adsorption mechanisms is ion exchange between H + from silanols (≡Si-OH) or/and Mg 2+ cations derived from the octahedral sheet in the sepiolite structure and the lanthanides or uranium cations. interactions between the oxygen from the silanol groups and the uranium ions. The anionic uranium complexes present at pH > 5 also play also a significant role in adsorption, as they interact with the alkyl chains of the surfactant cations attached to the sepiolite surface. In the case of lanthanides, the precipitation of lanthanide hydroxides Ln(OH) 3 also probably occurs at pH >8. Each of the mentioned mechanisms is feasible and its action is strongly dependent on the pH of the reaction environment.
The following reactions are possible:

Comparison of ODTMA-Sepiolite with Other Adsorbents
The adsorbent ODTMA-sepiolite proved be very effective for uranium ions' removal from aqueous solutions and sepiolite for lanthanides. The maximum adsorption capacity (q max ) is 285.6 mg/g for U(VI) and 91.6, 91.4, 104.9 mg/g for La(III), Eu(III), Lu(III), respectively. It is compared to those of the reported best uranium adsorbents ( Table 6) and much higher than those of commercial UO 2 2+ scavengers. The adsorption capacity (q max ) for achieving an equilibrium condition is an important parameter determining the sorption potential of an adsorbent towards a given analyte. It can be seen that the adsorption on ODTMA-sepiolite is much more effective than that of all compared adsorbents and very similar to the HDTMA-sepiolite case (212 mg/g), i.e., to sepiolite modified by hexadecyltrimethylammonium bromide [33]. The longer alkyl chain in the ODTMA cation structure and consequently, its higher hydrophobicity compared with HDTMA is the main factor affecting the partition of the uranyl ions between the aqueous and sepiolite phases. In turn, the lower capacity of the studied unnmodified sepiolite can be interpreted by the lack of surfactant on the surface and thus the absence of binding groups of uranium complexes. Therefore, these advantages combined with very high loading capacity, low cost, environmentally friendly nature, and facile syntheses make ODTMA-sepiolite promising for the removal and recovery of uranyl ions from aqueous solutions and sludge.
2. FTIR spectroscopy of the adsorption products show that the surfactant cations ODTMA + form a bilayer on the mineral surface; thus, there are electrostatic interactions of surfactant cations with the silicate framework of sepiolite, as well as Van der Waals ones of excessive ODTMA + cations with those already bound.
3. The TRLFS analysis of uranium adsorbed on the sepiolite surface points to at least two surface species of two short-and one long-lived ones. Their average fluorescence lifetime is: for short (τ1) and long-lived (τ2) forms of U-sepiolite: τ1 = 2420 ± 430 ns and τ2 = 37950 ± 5710 ns, for U-ODTMA-sepiolite: τ1 = 3523 ± 160 ns, and τ2 = 45400 ± 1830 ns. More water molecules in the coordination environment indicate a shorter lifetime of fluorescence due to their quenching by water molecules [23,25]. Thus, U(VI) forms two surface species on sepiolite that differ in the number of water molecules in the coordination environment.