Design, structural, spectral, DFT and analytical studies of novel nano
Scientific Reports volume 12, Article number: 17451 (2022) Cite this article
1439 Accesses
1 Citations
Metrics details
A novel nano-palladium (II) Schiff base complex (C1) is synthesized by the reaction between palladium chloride and the Schiff base N, N’-1, 2-phenylene) bis (3 -aminobenzamide (A1). The prepared compounds were characterized by elemental analysis, Ultraviolet–Visible spectroscopy (UV–Vis), Fourier transform infrared spectroscopy (FTIR), Scanning electron microscopy (SEM), Transmission electron microscopy (TEM) and Thermogravimetric Analysis (TGA). A combined solvent sublation-ICP OES methodology has been studied for the preconcentration, separation and determination of trace palladium (II) in media of diverse origin using the Schiff base ligand (A1). The different experimental variables that affect the sublation efficiency (S, %) were thoroughly investigated viz.: pH of sample solution; amounts of A1, Pd (II) and TBAB; type and amounts of surfactants, types of organic solvent, temperature and stirring time. The method involves the determination of trace palladium (II) after selective separation by solvent sublation, thus eliminating the effect of foreign ions and increasing the sensitivity. Also, palladium is determined directly in the organic phase, which decreases the determination time and its loss during determination. At optimum conditions, the linear range of Pd (II) was 10.0–100.0 ngmL−1. The coefficient of determination, the limit of detection (LOD) and limit of quantification (LOQ) were 0.9943, 21.29 ngL−1 and 64.5 ngL−1, respectively. This sublation method was applied to real samples and recoveries of more than 95% were obtained in the spiked samples with a preconcentration factor of 100. The mechanism of solvent sublatation of the TBA.[PdII-(A1)2] ion pairs is discussed. The computational studying was estimated to approve the geometry of the isolated solid compounds.
Palladium, as a precious metal, plays a very important role in modern industry due to its attractive physical and chemical properties such as excellent corrosion resistance, stable thermoelectricity and high catalytic activity. Palladium has been widely used in in electronics industry, in the production of dental and medicinal devices, in hydrogenation, dehydrogenation and organic synthesis and in automotive catalytic converters. It is reported currently that more than 50% of the world’s production of palladium are being consumed in production of auto-catalysts each year1 Due to the extended use of palladium in modern industries, the emission of this metal into the environment has increased considerably2 Under appropriate conditions, such as pH and redox potential, it is assumed that palladium undergoes methylation reactions in the aquatic environment and could be concentrated along the food chain, resulting in ecological and human health risks3,4 Consequently, establishing simple, highly sensitive and selective method for the determination of trace amounts of palladium in water samples is of great importance. However, it is often not possible to make direct determinations of palladium by employing the known analytical techniques due to its low or even extremely low concentration as well as matrix effects1 Pre-concentration and separation coupled with highly sensitive technique is one of the best ways to solve these problems. There are many approaches for preconcentration and separation, such as liquid–liquid extraction 5,6 solid phase extraction7,8,−9, ion exchange10,11 and HPLC12 and CPE13
A chelate extraction system is widely used for the pre-concentration of trace elements prior to atomic absorption spectrometric (AAS) determination. Hydrophobic chelating extractants have gained great interest for the separation of metal ions14. A flotation technique is also useful to separate inorganic ions from large volumes of sample solutions. Precipitate and ion flotation techniques have been developed to determine many kinds of elements with a high concentration ratio15,16,17,18,19,20. Recently, a solvent sublation technique21,22 has been developed and used as a combined method of flotation and solvent extraction23 with the advantages of both techniques.
Schiff base ligands provide a great platform in coordination chemistry for the development of numerous ligand systems with controllable binding to metal ions24,25,26. Ligands in this class could potentially stabilize metals in different oxidation states and induce stability in homogeneous and heterogeneous catalysts, which is particularly useful when they are viewed in catalytic activity perspectives27. Metal complexes derived from Schiff bases have found applications in different research areas, including and not limited to, molecular magnetism, catalysis and medical sciences28. Despite abundant reports regarding Schiff bases as ligands in the coordination chemistry of transition metals and their diverse applications, no research has been reported regarding palladium complexes supported with Schiff base ligands for solvent sublation of Pd (II). The present study is based on the fact that platinum group elements easily form their complexes with thio-organic compounds or long-chained alkyl amines29.
Bearing in mind the mentioned importance of palladium complexes and as a continuation of our recently published work30, the synthesis and characterization of nano-palladium (II) complex (C1) with the Schiff base N, N’-1, 2-phenylene) bis (3-aminobenzamide ligand (A1) are described in this paper.
A literature survey showed that no attempt has been found for using N, N’-1, 2-phenylene) bis (3-aminobenzamide Schiff base ligand (A1), TBAB, oleic acid surfactant (HOL) and MIBK in solvent sublation-ICPOES determination of palladium (II). In the present work, a number of experimental variables have been evaluated, e.g. pH, concentration of metal and ligand, temperature, etc. In addition to measurements of palladium (II) in synthetic sample, other samples such as river, seawater samples, were also analyzed. Moreover, density functional theory (DFT) studies were carried out to rationalize the experimental work and support the obtained results.
All the solvents and chemicals used were of analytical reagent grade and were used without purification. All glass wares were dipped into bidistilled water and dried in an oven at 80 °C. Palladium (II) chloride hydrated PdCl2.2H2O and % tetrabutylammonium bromide (TBAB) (99.5% purity) were obtained from Sigma Aldrich. Stock solution of 1 × 10−4 M Pd (II) was prepared by dissolving 0.00106 g PdCl2.2H2O in 100 ml of bidistilled water by adding 1.0 ml of concentrated HCl. Stock solution of 1 × 10−3 M of the Schiff base ligand (A1) chelating agent was prepared by dissolving 0.04385 g Schiff base ligand (A1) in 100 ml of ethanol. A stock solution of 6.36 × 10−2 M oleic acid (HOL) was prepared from the food-grade with sp. gr. 0.895 by dispersing 20 ml of HOL in one liter of kerosene. A stock solution of 0.1% tetrabutylammonium bromide (TBAB) was prepared by dissolving the solvent in bidistilled water.
For the solvent sublation technique, two types of flotation cells were used31. Type 1 was a cylindrical graduated glass tube of 16 mm inner diameter and 290 mm length with a stopper at the top and a stopcock at the bottom. This cell was used for adjusting the factors affecting the efficiency of the sublatation process. The second one was a cylindrical tube of 6.0 cm inner diameter and 45 cm length with a stopcock at the prime and was used for the separation of the studied analytes from the quite large volumes.
Elemental analyses (C, H, N, M) were performed using a Costech ECS- 4010- Analyzer.
The Fourier transform-infrared (FT-IR) spectra were recorded with a JASCO FT/IR-460 spectrophotometer with the use of KBr tablets in the range from 400 to 4000 cm−1 at room temperature.
Ultra violet visible (UV–Vis) spectra were gained for the prepared ligand (A1) and the complex (C1) by using a PerkinElmer 550 spectrophotometer in 1 cm quartz cell in ethanol over a range of 200–900 nm.
Traces of Pd (II) were detected by inductivity coupled plasma–optic emission spectroscopy (ICPOES) through a Varian spectrometer Model Varian Vista Pro, CCD Simultaneous. The optimum parameters are shown in (Table S1).
The Schiff base (A1) is prepared according to our recently published work30. The Schiff base (A1) was produced from refluxing a 3-aminobenzoic acid (3-ABA) (2.0 mmol, 0.2743 g) dissolved in 10 ml ethanol with 5 ml of 1, 2-phenylenediamine (Phen) (1.0 mmol, 0.1081 g) dissolved in ethanol in the presence of 2 drops of glacial acetic acid (1 M) for 2 days at 75 °C according to reaction synthesis32,33, Fig. 1. During the reaction, the color of the prepared solution was changed from the pale yellow to the formed reddish-brown precipitate. This formed precipitate was filtered off, washed several times with water/ ethanol, and afterward dried under a vacuum.
Synthesis of the Schiff base ligand (A1).
Nano-palladium Schiff base complex (C1) was synthesized via refluxing PdCl2.2H2O (1.0 mmol, 0.2134 g) dissolved in 10 ml distilled water (DW) with ligand (A1) for 2 days at 75 °C. Afterwards the system was refluxed. During the reaction, the color of the solution was changed from reddish-brown to a dark red precipitate. The precipitate was filtered off, washed several times with water/ ethanol, and finally dried under a vacuum.
Geometry optimizations and other DFT calculations were performed on the Schiff base (A1) ligand and its palladium complex (C1) using B3LYP level of theory, Becke’s three parameter (B3) non local exchanges with the correlation functional of Lee, Yang, and Parr (LYP)34. We used the B3LYP level to study electronic compounds because the predicted geometries are very reliably and provide good estimations for HOMO–LUMO gaps, in a good agreement with experimental values30,35,36,37,38,39,40,41. All the calculations were carried out by using 6–31 g (d) basis set for O, N, C and H atoms and lanl2dz basis set was used for Pd atom. All computations were carried out by using Gaussian09 suite of program42. Gauss View 5.0 package was used to obtain various graphic views of molecular shapes of distinctive molecular.
In an Erlenmeyer flask, 2 mL of 1.88 × 10−5 mol L−1 (A1) solution was added to an aliquot containing 0.94 × 10−6 molL−1 of Pd (II); the pH was adjusted by 0.5 mol L−1 HCl and or 0.5 mol L−1NaOH and the solution was mixed completely. A red color of C1 developed instantaneously. Two ml of 4 × 10−4 molL−1 of TBAB solution were added and the mixture was shaken well for 2 min to allow complete development of the TBA.[PdII-(A1)2] ion pairs. All contents were quantitatively transferred into a flotation cell (type 1) and the volume was adjusted to 10 mL. Then, 2 mL of 2 × 10−4 mol L−1 HOL was added. The flotation cell was shaken upside down for 2 min. Vigorous shaking of the flotation cell in the presence of the surfactant (HOL) created bubbles in the solution which enhanced the floatability of the TBA.[PdII-(A1)2] ion pairs. 5 mL of MIBK were added to the solution surface and the flotation cell was shaken upside down by hand. The red TBA.[PdII-(A1)2] ion pairs were quantitatively extracted into the organic layer on the solution surface. The aqueous phase was run off through the bottom of the cell.
After complete sublatation (10 min) the scum layer was evaporated to half volume by heating in a water bath. It was then made up to 10 mL in a volumetric flask using a solution containing 20:80, 1.0 mol L−1 HNO3/10% v/v methanol and analyzed by ICP OES to measure the concentration of Pd(II) at λmax 340.4 nm with axial viewing.
The solvent sublation efficiency (S %) of Pd (II) was determined from the following relationship:
Here, Co and Ci denote the concentration of Pd (II) in the organic and in the initial aqueous layers, respectively.
Alternatively, Pd (II) was determined directly by ICP OES in the aqueous mother liquor. The separation efficiency (S %) of the analyte was calculated from its concentration in the mother liquor according to the relation
where ci and cf denote the initial and final concentrations of the analyte, respectively.
Both A1 and C1 are stable colored compounds, slightly soluble in DMF and soluble in DMSO. The most important obtained physical and microanalytical data for the prepared compounds are summarized in Table 1. Melting point is ~ 174.1 °C for A1 and > 300 °C for C1; the yields of A1 and C1 are 96.5 and 82.1%, respectively.
A1 is dissociated to A1− and H+ and the unshared electron pairs of –O– and = N– in A1 takes part in a coordination bond with metal ions. Anionic metal complex is formed in the presence of excess A1; and the anionic complex forms ion pairs with TBA+ ion by the addition of tetra-n-butyl ammonium bromide solution43.
The elemental analyses of the Schiff base A1, the Pd(II)-A1 complex (C1) and the [TBA-Pd(II)-A1] ion pairs (C2), are presented in Table 1. The obtained results were in agreement with that calculated for the suggested formula. Anal. Calc. (%): for A1; C24H30N4O4; (438.53 g/mol); C, 65.73; H, 6.90; N, 12.78; found C, 65.94; H, 6.73; N, 12.89. Whereas, Anal. Calc. (%): for C1; C24H28N4O4Pd; (542.93 g/mol); C, 53.09; H, 5.20; N, 10.; found C, 53.19; H, 5.31; N, 10.22.
The FTIR spectra of the ligand A1, the complex C1 in aqueous solution, TBA.[Pd (A1)] (C2) ion associate in organic layer are presented in Fig. 2a,b,c,d. The most significant frequencies of A1, C1 and C2 are presented in Table 1. As it has already been mentioned earlier, the IR of A1(Fig. 2a) exhibits an absorption broad band in the range between 3635–3278 cm−1 which can be recognized to the υ(OH) of the alcohol, υ(OH), υ(NH) of keto-enol form and υ(NH2) 44,45. The band at 2935 cm−1 is assigned to υ(CH)-sp3. The bands between 1730–1440 cm−1 can be attributed to υ(C = O), υ(C = N) and ν(C = C) and the broad bands due to the formation of the two forms of keto and enol structures. The band that appeared at 1385 cm−1 is due to ν(C–N) groups. The bands between 1330 and 736 cm1 are due to aromatic CH46. The IR spectrum of the C1 complex, Fig. 2b, proves the complexation of the ligand A1 with the metal ion. In contrast to the spectrum of the free ligand A1, the IR of the complex C1 shows a significant shift of υ(OH),ν(NH), υ(C = N) and υ(C–N) vibrations. While, the υ(C = O) and υ(C = C) vibrations stay at more or less at the same place, which designates that (C = C) does not contribute in coordination with the metal ion. So, A1 acts as a neutral bidentate coordination site via υ (OH), (C–N), (C = O), and azomethine nitrogen (C = N) atoms. This observation is additionally supported by new bands that were found at 671 and 436 cm−1 that can be assigned to υ (Pd–O) and υ(Pd–N), respectively47.
The FTIR spectra of (a) the ligand A1, (b) C1 complex in aqueous solution, (c) TBA.[PdII-(A1)] (C2) ion pair in aqueous layer and (d) TBA.[PdII-(A1)](C2) ion associate in organic layer.
The IR spectrum of the C2 ion pair in aqueous solution, Fig. 2c, is different from the IR spectra of A1 and C1, Fig. 3a,b, reflecting that there is chemical contribution between TBAB and the C1 complex as –NH2 stretching band disappeared and new –NH stretching band appeared. This means that protonation occurred by the release of hydrogen atom of (–NH2) carrying positive charge with Br− atom of TBAB carrying negative charge, so electrostatic bonding has been formed.
The electronic absorption spectra of (a) Schiff base ligand (A1), (b) Pd complex ( C1) in aqueous solution and (c) TBA.[Pd (A1)] ion associate in organic layer.
Finally it was noticed that the IR spectrum of the TBA.[ PdII-(A1)] (C2) ion pair isolated in the aqueous solution, (Fig. 2c) and in the organic layer, (Fig. 2d) are identical denoting that the process of sublation could be physical in nature.
The electronic absorption spectra of A1 and C1were showed in Fig. 3. From Fig. 3, it was recognized that the A1 (Fig. 3a) exposes three absorption bands at 226, 296, and 440 nm, which were agreed to intra ligand charge transfer (n–π* and π–π*). While, the C1 exposes four absorption bands at 236, 268, 274, and 510 nm, which were agreed to the ligand–metal charge transfers transitions (LMCT) and owing to the intra-ligand charge transfers (n–π* and π–π*)48,49,50,51,52.
The absorption spectra of the C1 in the aqueous solution and in the organic layer are completely different from that of A1. It is observed that: 1) the λmax of C1 exhibits a red shift (70 nm) from that of A1 and 2) the absorbance of C1-HOL-MIBK system exhibits nearly 4-folds that of C1 in aqueous solution. This proves that the species are highly concentrated in the presence of HOL and MIBK.
Scanning electron microscopy (SEM) and Transmission electron microscopy (TEM) were employed to characterize the micromorphology and the size and shape of nanoparticles. As shown in the SEM image (Fig. 4a), the nano-palladium (II) complex (C1) complex nanoparticles were present as uniform particles with spherical and ovoid morphology. From the TEM micrographs (Fig. 4b,c), the average particle size of C1 nanoparticles is estimated between 72.0 to 97.0 nm.
a SEM of C1; b & c TEM of C1.
The optimized geometry of the Schiff base (A1) ligand and its palladium complex (C1) are shown in Fig. 5. Highest Occupied Molecular Orbitals (HOMO) and Lowest Unoccupied Molecular Orbitals (LUMO) are very considerable elements of theoretical molecular design53. The HOMO is electron donor and LUMO the electron acceptor sites and the molecular hardness and softness of a compound can be predicted from the HOMO–LUMO gap54.
Optimized structures, HOMO and LUMO based on DFT calculations by using B3LYP method with 6–31 g (d) basis sets.
The Global Reactivity Parameters39,40,41 such as ionization potential (IP), electron affinity (EA), hardness (\(\eta )\), softness (\(\sigma\)) and electronegativity (\(\chi\))] can be determined from the HOMO and LUMO orbital energies through Koopman’s theorem 55. The ionization potential (IP) and electron affinity (EA) are defined as the negative of HOMO and LUMO energies, respectively (IP = − EHOMO and EA = − ELUMO). The chemical hardness (\(\eta )\) is a measure of resistance of an atom against the charge transfer 56. It can be computed using the IP and EA energies:
The softness (\(\sigma\)), which is the reciprocal of hardness (\(\sigma = \frac{1}{\eta }\)), is a property of its capability to accept the electron.
Thus, a structure becomes harder (softer) when its energy gap (ΔE(LUMO–HOMO)) is getting wider (narrower). The electronegativity (\(\chi\)) in terms of IP and EA are given by:
The higher reactivity of the Pd-complex (C1) over the Schiff base ligand (A1) is explained in the light of energy gap, ΔE(LUMO–HOMO), which measures the reactivity; as the energy gap decreases the reactivity increases and the amount of electronic charge transferring from (A1) to the central metal ion increases. Table 2 illustrates that ΔE (LUMO–HOMO) for Pd-complex (C1) was found to be more reactive than of the Schiff base ligand (A1). Hard molecules (\(\eta )\) have a large energy gap, and soft molecules (\(\sigma\)) have a small energy gap57,58. A soft molecule is more reactive than a hard molecule because a soft molecule has a lower ΔE (LUMO–HOMO)59. From Table 2, C1 is softer than A1 and this confirms that C1 is more reactive than L1. The \(\chi\) is a measure of power of atom(s) to attract the electrons60. A high value of electronegativity (χ) for C1 suggests strong ability to attract electrons from the A1, which leads to greater interaction to form the complex C1. Finally, the dipole moment (μ) is a factor that can also provide information about interaction between A1 molecule and Pd. The value (μ) of Pd–complex (C1) is higher than (μ) of the Schiff base ligand (A1); this suggests the stronger interactions between A1 and Pd to form the complex. It was observed that there is charge density transferred from Schiff base atoms to metal ion and there is electrons back-donation from the metal ion to the donating atoms on the Schiff base after complexation. The (EHOMO), (ELUMO), energy gap ΔE(LUMO–HOMO), ionization potential (IP), electron affinity (EA), hardness (\(\eta\), softness (\(\sigma\)), electronegativity (\(\chi\)) and dipole moment (μ) of the Schiff base (A1) and the Pd-complex (C1) are listed in Table 2.
Solvent sublation depends on the solubility of the metal-complex in an organic solvent. But the solvent should be immiscible with an aqueous phase, non-volatile and lighter than the aqueous solution. It must be kept at the surface of the solution in a stable state. The sublation efficiencies were compared with several water-immiscible and light solvents such as methylisobutyl ketone (MIBK), diisopropyl ketone (DIPK), cyclohexane, benzene and o-xylene, having 0.77–0.89 g/mL densities. MIBK showed good sublation efficiencies for similar levels and was used in subsequent studies.
Before analysis of the standard and real samples by ICP OES, convenient conditions of the instrument should be obtained. Thus, different parameters influencing the intensity of signals in ICP OES such as radio frequency (rf), generator power, nebulizer pressure, viewing height of plasma, auxiliary gas flow rates and peristaltic pump rate were optimized. Then, to guarantee that maximum extraction efficiency was obtained, the parameters affecting solvent sublation efficiency including metal, surfactant and chelating agent concentration, shaking time and temperature, pH of solution and sample volume were optimized. The optimized conditions of ICP OES are given in Table S1.
The digital photographs of the TBA.[PdII-(A1)] ion pairs in the aqueous solution and in the organic layer are shown in Fig. 6. As it can be clearly seen, the ion pair has a clear homogenous red color in the aqueous solution (Fig. 6a). After the successful sublation of the ion pair, the red colored TBA.[PdII-(A1)] ion pair is concentrated in the organic layer on the top of solution surface while the rest of the solution becomes colorless as it can be noticed in Fig. 6d.
Digital photographs of the sublation process. a) TBA.[PdII-(A1)] ion pair in aqueous solution; b) & c) TBA.[PdII-(A1)] ion pair after addition of HOL; d) TBA.[PdII-(A1)] ion pair sublated to the MINK organic layer.
The formation of C1 complex was influenced by solution pH and Pd (II) ions can form hydroxide precipitates in a strongly basic solution. The completeness of complex formation was investigated by changing the pH from 2 to 7 (Fig. 7). The sublation of the Pd (II) was very low in the acidic range of pH 2–3 because the analyte could not be extracted into MIBK. This is due to the difficult formation of complexes because A1 is nearly non ionized in such an acidic solution. Hydroxide precipitates also were not formed in this range. A series of experiments was carried out to study the effect of pH on the sublation efficiency (S%) of Pd (II) (2 × 10−6 mol L−1) with 5 ml of 1 × 10−3 mol L−1 TBAB, 2 × 10−3 mol L−1 HOL and 5 ml MIBK in the absence and in the presence of 2 × 10− mol L−1 of A1. The data in Fig. 7, curve a, prove that in the absence of the ligand A1, the maximum separation efficiency doesn't exceed 30% at all pH values tested. Such separation percent is not satisfactory from the analytical point of view. On the other hand, Fig. 7, curve b, shows that complete separation (≈100%) of Pd (II) was obtained at pH 4.0 in the presence of 2 × 10−4 mol L−1 of A1. Further experiments were carried out at pH 4.0.
Effect of pH on sublation efficiency of Pd (II); (a) in the absence of A1; (b) in the presence of 2.0 × 10−4 mol L−1 A1 by using 5 × 10−4 mol L−1 TBAB; 2 × 10−3 mol L−1 HOL; MIBK (5 ml) at room temperature.
The effect of ligand concentration on the sublation efficiency (S% ) of a 1.0 × 10−6 mol L−1 of Pd(II) was investigated at pH 4.0 using 5 ml of 1 × 10−3 mol L−1 TBAB, 2 mL of 2 × 10−3 mol L−1 HOL, 5 ml MIBK and various amounts of A1. The sublation efficiency (S%) increases with increasing ligand concentration untill it reaches its maximum at 2.0 × 10−6 mol L−1 of A1; at this concentration the molar ratio is 1:2 Pd (II):A1. The results given in Fig. 8 show that excess ligand amount had no drastic effect on the sublation process.
Influence of A1 concentration on the sublation efficiency of 1.0 × 10−6 mol L−1 Pd (II) at pH 4.0 using 5 × 10−4 mol L−1TBAB; 2 × 10−3 mol L−1 HOL; MIBK (5 ml).
To confirm the previous data, another series of experiments was carried out by fixing the ligand concentration and changing the metal concentration from 1.0 to 5.0 × 10−6 mol L−1). The results obtained showed that complete separation occurs at the same previous ratio of 1:2 Pd (II): A1. Above such a ratio, increasing Pd (II) concentration results in decrease of the separation efficiency. This reflects that insufficient ligand is present for complete complexation and indirect separation.
As described earlier, Pd (II) ions form anionic complex with an excess of A1 and this anionic complex forms ion pairs with the TBAB. The amount of the TBAB affects the stability of the TBA.[PdII-(A1)] ion pair. Under other optimum conditions, the efficiency of solvent sublation of 1.0 × 10−6 mol L−1 Pd (II) was investigated by changing the TBAB concentration in the presence of 2.0 × 10−5 mol L−1 of A1, 2 × 10−3 mol L−1 HOL and 5 ml MIBK at pH 4.0. The results in Fig. 1S, show that the maximum sublation efficiency (S %) of TBA. [PdII-(A1)] was attained when the concentration of TBAB was ≥ 2 × 10–4 mol L−1. Thus, a 5 ml of 4 × 10−4 mol L−1 of TBAB was chosen in the present study.
In general, a surfactant is added to float some materials in an aqueous solution by making them hydrophobic. Hydrophobic materials can be more effectively seeded from aqueous solutions than hydrophilic materials. The material can be a precipitate, complex ions or ion associate (ion pairs) species. TBA. [PdII-(A1)] was the ion pair in the present sublation methodology.
In the present study, the efficiency of sublation by the type of surfactant was evaluated using anionic (HOL), non-ionic TX-80 and the cationic (CTAB) surfactants. The TBA.[PdII-(A1)] ion associate was not sublated at all upon using the cationic or the nonionic surfactants. On the other hand, the sublation efficiency (S %) reaches its maximum on using the HOL anionic surfactant. Such phenomenon can be interpreted to mean that excess TBA+ around PdII-(A1)− complex creates the ion pairs of positive charge. Therefore, the addition of the anionic surfactant improves the efficiency of sublation.
The concentration of HOL is an important parameter; up to a limit the separation percentage increases as the concentration of the surfactant increases. The effect of HOL concentration on the sublation efficiency of TBA.[PdII-(A1)] ion pairs were investigated. The results obtained indicated that the sublation efficiency of TBA.[PdII-(A1)] ion pair reaches its maximum (100%) over a wide range of HOL concentrations (1 × 10−3 to 1 × 10−4 mol L−1) until its critical micelle concentration (CMC) is reached. At a higher HOL concentration, there will be a concentration, at which the surfactant molecules gather together to form a microball, called micelle. Micelles compete for the ion pairs and since they stay in solution, they reduce the effectiveness of separation. The concentration of the surfactant also changes the bubble size with the size getting smaller as the surfactant increases. This makes creamier foam. A suitable concentration (2X10−3 mol L−1) of HOL was selected throughout this work.
To study the role of temperature on the Pd (II) separation, Pd (II), surfactant and A1 solutions were either heated or cooled to the same temperature. A1, TBAB and HOL are quickly poured into the Pd (II) solution at zero time. The solution was introduced into flotation cell Jacketed with 1 cm thick fiberglass insulation. The sublation steps were preceded as previously mentioned at pH≈4. The results obtained, Fig. 2S, indicated that the sublation of TBA.[PdII-(A1)] is not affected by raising the temperature up to 40 °C above which the sublation efficiency starts to decrease. The decrease in the sublation efficiency upon increasing the temperature may be attributed to the instability of the ion pairs TBA.[PdII-(A1)] as well as the weak binding between the HOL surfactant and the ion associate species. A finding, that helps to explain the mechanism of sublation of the TBA.[PdII-(A1)] ion associate species by the HOL surfactant and MIBK. The whole work has been carried out at room temperature (25 ± 1 °C).
A proper shaking is required for complete complexation of A1 with palladium ions, which forms hydrophobic complex after around 2.0 min and remains constant until 48.0 h, as shown in Fig. S3. For the following work, a shaking time of 60.0 s followed by a rest period of 3.0 min was used.
A series of experiments were conducted to sublate a fixed concentration of the analyte (1.0 × 10−6 mol L−1 of palladium) from different aqueous volumes (50–1500 ml) using suitable large flotation cells under the recommended conditions. It is clear from the data in Fig. 4S that, 10−6 mol L−1 of the analyte can be quantitatively separated from different aqueous volumes up to 1 L using 10 mL of the organic layer. The enrichment factor (preconcentration factor)61, defined as the ratio of the volumes before and after solvent sublation, was 100.
Table 2S summarizes the effect of ionic strength on the separation efficiency of Pd (II) under the recommended conditions. Sodium, magnesium and calcium as chloride and sulfate were added during the sublation separation of the analyte at the recommended conditions. It was found that these salts, even up to 0.5 mol L−1 concentration have no effect on the solvent sublation efficiency of the analyte.
In the view of the high selectivity provided by ICP-OES, the interferences studied were related to the pre-concentration step. The effect of foreign metal ions on the solvent sublation of Pd (II) with A1 has been studied in detail. The obtained results reveal that in spite of the high tendency of A1 to form complexes with different transition metal ions, fortunately, most of these complexes are not sublated with the Pd (II) complex at pH 3.5–4.0. The experimental data showed that although some foreign ions have little interfering effects (∼3%), Table 3, all of these interferences were completely controlled by adding excess A1 (2 × 10−4 mol L−1). Hence, one can predict that the interfering effects may be due to complex formation which is accompanied by a decrease in the ligand concentration. Consequently, masking of the interfering effects by adding excess A1 offers a highly selective procedure for the separation and determination of microamounts of Pd (II) in various complex materials, like environmental and biological samples.
Under the optimum conditions, the calibration graph was linear in the range 10.0–1000.0 ng mL-1. The calibration equation is y = 2.6696x (μg mL−1) + 0.0415, with a correlation coefficient of 0.9943. The limit of detection62, (defined as LOD = 3 SB/m, where SB and m are standard deviation of the blank and the slope of the calibration graph, respectively), was 21.29 ngL−1. The limit of quantification (LOQ) calculated as 3 LOD was 64.5 ngL−1. The relative standard deviation was 0.023% (c = 5.0 μg mL−1, n = 3). The analytical characteristics of this technique are shown in details in Table 4.
The optimized experimental conditions were applied to real samples to evaluate the efficiency of the combined solvent sublation-ICP-OES method for the pre-concentration and determination of trace Pd (II) ions. The calibration curves were prepared with the standard solutions. The standard solutions (1.0 L) were treated under the experimental conditions optimized above.
The proposed method was applied to determination of trace amounts of palladium in synthetic samples and the palladium catalyst waste water with satisfactory results, Table 5.
In order to investigate the applicability to a natural-water samples, the recoveries of known amounts of Pd (II) added to bidistilled, river and sea water samples were examined by such a procedure. To 20 ml aliquots of clear uncontaminated, filtered water samples 1, 3 and 5 μg of Pd (II) were added and the pH was adjusted by HCl to pH 4.0. The as previously mentioned solvent sublation –ICP OES methodology was applied. The recoveries obtained, Table 6, were in the range of 98.00–99.42%. These results indicate that this analytical method could be successfully applied to the determination of trace Pd (II) in real water samples.
According to Sebba63, the separation mechanism in the solvent sublation technique is very simple. As the gas bubbles pass through the liquid mass they collect the colligend-collector species, which is then transferred to the organic phase on the upper surface of the liquid mass. In studies concerning separation via sublation, the role of surfactant is very important. The nature of the interaction between oleic acid surfactant and the formed TBA+PdII-(A1)2− ion-pair must be studied to approach the actual mechanism of sublation. An ion pair is a pair of oppositely charged ions held together by Coulomb attraction without formation of a covalent bond. The proposed mechanism may proceed through: i) a physical interaction through Van der Waal; ii) by forming a hydrogen bond between the hydrophilic part of the surfactant and the active sites in the ligand complex or iii) by an interaction between oleic acid and the ion pair, formed in solution through a coordinate bond, forming a self-floatable [TBA+.[PdII-(A1)−-HOL) species. In all cases, the hydrophobic part of the surfactant attaches to air bubbles and floats separating the analyte-containing species.
As it has been mentioned earlier in this study, A1 forms anionic complex with Pd (II) and the addition of sufficient amount of TBAB turned this anionic complex into a positively charged ion pair that was easily made hydrophobic by the addition of HOL, floated by vigorous shaking of the flotation cell and extracted into the MIBK.
In the present investigation, the mechanism of sublation is proposed to be physical in nature. This suggestion may be attributed to the following findings:
The sublated species in the organic layer has the same colour (red) as that obtained in the aqueous solution (especially in high reactants concentrations).
The sublation efficiency was greatly affected by temperature. Raising the temperature above 40 °C results in a marked depression in the sublation efficiency of the TBA.[PdII-(A1)] ion associate complex. This behavior can be attributed to the weak binding between the ion pair and oleic acid reflecting that there is no coordinate or hydrogen contribution between HOL and the TBA.[PdII-(A1)] ion associate. Also, the physical force between HOL and TBA.[PdII-(A1)], can easily be destroyed by heat.
Finally it was noticed that the IR spectra of the TBA.[PdII-(A1)] ion associate isolated in the aqueous solution, (Fig. 2c) and organic layer, (Fig. 2d), are identical denoting that the process of sublation could be physical in nature.
In conclusion, all of the mentioned studies suggest the first proposal mechanism.
A comparison between the analytical performances of the present approach and other previous reports in the kinds of literature for the determination of palladium is presented in Table 7. The analytical figures of merits of our work are comparable or better than previously reported reports.
In this paper, nanopalladium(II) complex of the 1-N, N’-1, 2-phenylene)bis(3-aminobenzamide) Schiff base ligand (A1) was synthesized and characterized by elemental analysis, spectroscopy techniques and physical measurements. The results showed that the A1acted as a neutral bidentate ligand. Trace Pd(II) in several water samples of adjusted pH 4.0 were determined by a solvent sublation using an ion pair of PdII(A1)− anion and tetrabutylammonium ion for the utilization of a synergistic effect. The hydrophobic ion pairs created by the addition of oleic acid were floated and extracted into MIBK by vigorous shaking of the flotation cell. This procedure was applied to the analysis of several real water samples and recoveries of more than 95% were obtained in spiked samples of given amounts of analytes. The RSD of less than 3% was obtained for standard spiked samples. Such results show that this is a fairly accurate and reproducible method and can be applied to similar samples. The results show that the solvent sublation pretreatment is a sensitive, rapid, simple and safe method for the separation/preconcentration of palladium. Also, DFT calculations were done to predict the host-gust interaction between the Schiff base and Pd (II) cations.
All data generated or analysed during this study are included in this published article.
Dubiella-Jackowska, A., Polkowska, Z. & Namieśnik, J. Platinum group elements: A challenge for environmental analytics. Polish J. Environ. Stud. 16, 329–345 (2007).
CAS Google Scholar
Barefoot, R. R. Distribution and speciation of platinum group elements in environmental matrices. TrAC - Trends Anal. Chem. 18, 702–707 (1999).
Article CAS Google Scholar
Ravindra, K., Bencs, L. & Van Grieken, R. Platinum group elements in the environment and their health risk. Sci. Total Environ. 318, 1–43 (2004).
Article ADS CAS PubMed Google Scholar
Point, U. C. Determination of Palladium in water samples using cloud point extraction coupled with laser thermal lens spectrometry. J. Korean Chem. Soc. 59, 407. https://doi.org/10.5012/jkcs.2015.59.5.407 (2015).
Article CAS Google Scholar
Shamsipur, M., Ramezani, M. & Sadeghi, M. Preconcentration and determination of ultra trace amounts of palladium in water samples by dispersive liquid-liquid microextraction and graphite furnace atomic absorption spectrometry. Microchim. Acta. 166, 235–242 (2009).
Article CAS Google Scholar
Limbeck, A., Rendl, J. & Puxbaum, H. ETAAS determination of palladium in environmental samples with on-line preconcentration and matrix separation. J. Anal. At. Spectrom. 18, 161–165 (2003).
Article CAS Google Scholar
Godlewska-Zyłkiewicz, B. Preconcentration and separation procedures for the spectrochemical determination of platinum and palladium. Microchim. Acta. 147, 189–210 (2004).
Article Google Scholar
Mladenova, E., Karadjova, I. & Tsalev, D. L. Solid-phase extraction in the determination of gold, palladium and platinum. J. Sep. Sci. 35, 1249. https://doi.org/10.1002/jssc.201100885 (2012).
Article CAS PubMed Google Scholar
Venkatesh, G. & Singh, A. K. Enrichment and flame atomic absorption spectrometric determination of palladium using chelating matrices designed by functionalizing Amberlite XAD-2/16 and silica gel. Microchim Acta. 159, 149–155 (2007).
Article CAS Google Scholar
Kovacheva, P. & Djingova, R. Ion-exchange method for separation and concentration of platinum and palladium for analysis of environmental samples by inductively coupled plasma atomic emission spectrometry. Anal. Chim. Acta. 464, 713 (2002).
Article Google Scholar
Moawed, E. A. Preparation of novel ion exchange polyurethane foam and its application for separation and determination of palladium in environmental samples. Anal. Chim. Acta. 580, 263–270 (2006).
Article CAS PubMed Google Scholar
Lin, H., Huang, Z. J., Hu, Q., Yang, G. & Zhang, G. Determination of palladium, platinum, and rhodium by HPLC with online column enrichment using 4-carboxylphenyl-thiorhodanine as a precolumn derivatization reagent. J. Anal. Chem. 62, 58–62 (2007).
Article CAS Google Scholar
Akl, M. A., AL-Rabasi, A. S. & Melouk, A. F. Cloud Point Extraction and FAAS Determination of Copper (II) at Trace Level in Environmental Samples using N-benzamido-N’-benzoyl thiocarbamide and CTAB. Egypt. J. Chem. 64, 313–322 (2021).
Google Scholar
Purnamawaty, E., Amimoto, T., Imura, H., Usui, Y. & Ohashi, K. Extraction equilibrium of Molybdenum (VI) with several alkylated 8-Quinolinol derivatives. Anal. Sci. 10, 749–753 (1994).
Article CAS Google Scholar
Hiraide, M., Yoshida, Y. & Mizuike, A. J. Flotation of traces of heavy metals coprecipitated with Aluminum hydroxide from water and sea water. Anal. Chim. Acta. 81, 185 (1976).
Article CAS Google Scholar
Hiraide, M., Uchida, T. & Kawaguchi, K. Determination of trace amounts of heavy metals in alumina by electrothermal atomic absorption spectrometry after diethyldithiocarbamate extraction and matrix precipitation. Jpn. Analyst. 118, 537–539 (1993).
Article ADS CAS Google Scholar
Fukuda, K. & Atsushi, M. Separation of traces of silver by the coprecipitation-flotation method. Bunseki Kagaku 17, 319–322 (1968).
Article CAS Google Scholar
Hiraide, M. & Mizuike, A. Separation and preconcentration of trace substances—III Flotation as a preconcentration technique. Pure Appl. Chem. 8, 1555. https://doi.org/10.1351/pac198254081555 (1982).
Article Google Scholar
Sekine, K. Froth flotation separation of small amounts of thorium by means of Arsenazo III and Zephiramine. Fresenius Z. Anal. Chem. 273, 103–107 (1975).
Article CAS Google Scholar
Aoyama, M., Hobo, T. & Suzuke, S. J. Ion flotation-spectrophotometric determination of trace amounts of nitrite ion in waters. Anal. Chem. Acta. 31, E105. https://doi.org/10.2116/bunsekikagaku.31.3_E99 (1981).
Article Google Scholar
Kotsuji, K. K., Arikawa, Y. M. & Hayash, S. Spectrophotometric determination of iron using solvent sublation method. Talanta 26, 475–479 (1977).
CAS Google Scholar
Kim, Y. S., Shin, J. H., Choi, Y. S., Lee, W. & Lee, Y. I. Solvent sublation using 8-hydroxyquinoline as a ligand for determination of trace elements in water samples. Microchem. J. 6, 99–107 (2001).
Article Google Scholar
Kim, Y. S., Sin, J. H., Choe, Y. S., Lee, W. & Lee, Y. I. Solvent sublation of trace noble metals by formation of metal complexes with 2-mercaptobenzothiazole. Bull. Korean Chem. Soc. 22, 19–24 (2001).
CAS Google Scholar
Gennari, C. & Piarulli, U. Combinatorial libraries of chiral ligands for enantioselective catalysis. Chem. Rev. 103, 3071–3100 (2003).
Article CAS PubMed Google Scholar
Cozzi, P. G. Metal-Salen Schiff base complexes in catalysis: Practical aspects. Chem. Soc. Rev. 33, 410–421 (2004).
Article CAS PubMed Google Scholar
Hossain, S. M. et al. Synthesis and characterization of a novel, ditopic, reversible and highly selective, ‘‘Turn-On” fluorescent chemosensor for Al3+ ion. RSC Adv. 5, 63338–63344 (2015).
Article ADS CAS Google Scholar
Makio, H., Kashiwa, N. & Fujita, T. FI catalysts: A new family of high performance catalysts for olefin polymerization. Adv. Synth. Catal. 344, 477. https://doi.org/10.1002/1615-4169(200207)344:5%3c477::AID-ADSC477%3e3.0.CO;2-6 (2002).
3.0.CO;2-6" data-track-action="article reference" href="https://doi.org/10.1002%2F1615-4169%28200207%29344%3A5%3C477%3A%3AAID-ADSC477%3E3.0.CO%3B2-6" aria-label="Article reference 27" data-doi="10.1002/1615-4169(200207)344:53.0.CO;2-6">Article CAS Google Scholar
Pasatoiu, T. D. et al. Preparation, crystal structures, and magnetic features for a series of dinuclear [NiIILnIII] Schiff-base complexes: Evidence for slow relaxation of the magnetization for the DyIII derivative. Inorg. Chem. 50, 5890. https://doi.org/10.1021/ic2004276 (2011).
Article CAS PubMed Google Scholar
Barefoot, R. R. Determination of platinum at trace levels in environmental and biological materials. Environ. Sci. Technol. 31, 309. https://doi.org/10.1021/es960712i (1997).
Article ADS CAS Google Scholar
Akl, M. A., El-Gharkawy, E. R., El-Mahdy, N. A., El-Sheikh, S. M. & Sheta, S. M. A novel nano copper complex: potentiometry, DFT and application as a cancer prostatic biomarker for the ultrasensitive detection of human PSA. Dalton Trans. 49, 15769–15778 (2020).
Article CAS PubMed Google Scholar
Kabil, M. A., Ghazy, S. E., El-Asmy, A. A. & Sherif, Y. E. Highly selective procedure in its allied materials for trace analysis of Platinum (IV) in its allied materials. Anal. Sci. 12, 431–437 (1996).
Article CAS Google Scholar
Şabik, A. E., Karabörk, M., Ceyhan, G., Tümer, M. & Dığrak, M. Polydentate schiff base ligands and their La(III) complexes: Synthesis, characterization, antibacterial, thermal, and electrochemical properties. Int. J. Inorg. Chem. 2012, 1. https://doi.org/10.1155/2012/791219 (2012).
Article CAS Google Scholar
Hussain, Z., Yousif, E., Ahmed, A. & Altaie, A. Synthesis and characterization of Schiff’s bases of sulfamethoxazole. Org. Med. Chem. Lett. 4, 1–4 (2014).
Article PubMed PubMed Central Google Scholar
Becke, A. D. Density-functional thermochemistry. III. The role of exact exchange. J. Chem. Phys. 98, 5648. https://doi.org/10.1063/1.464913 (1993).
Article ADS CAS Google Scholar
Ammar, H. Y. & El-Gharkawy, E. S. R. Adsorption of NO molecule on oxygen vacancy-defected MgO nanotubes: DFT study. Eur. J. Sci. Res. 120, 401–415 (2014).
Google Scholar
El-Gharkawy, E. R. H. & Ammar, H. Y. Adsorption of CO on TM-deposited (MgO) 12 nano-Cage (TM= Ni, Pd and Pt): a study on electronic properties. J. Nanoelectron. Optoelectron. 13, 546–553 (2018).
Article CAS Google Scholar
Sheta, S. M., Akl, M. A., Saad, H. E. & El-Gharkawy, E. R. H. A novel nano-lanthanum complex: Synthesis, characterization and application as a macrofuran chemosensor in pharmaceutical, biological and environmental samples. RSC Adv. 10, 5853–5863 (2020).
Article ADS CAS PubMed PubMed Central Google Scholar
Abd El-Maksoud, S. A., El-Dossoki, F. I., Migahed, M. A., Gouda, M. M. & El-Gharkawy, E. R. H. New Imidazol-1-ium Bromide derivative surfactants as corrosion inhibitors for carbon steel in 1 M HCl solutions: Experimental and theoretical studies. J. Bio. Tribo. Corros. 7, 1–15 (2021).
Article Google Scholar
Lakshmi Praveena, P., Ramakrishna, D. S. & Durga, P. UV spectral characterization of a smectic-C liquid crystal: Theoretical support to the experiment. Mol. Cryst. Liq. Cryst. 643, 76–82 (2017).
Article Google Scholar
Veligeti, R., Ramakrishna, D. S., Madhu, R. B. & Anireddy, J. S. Synthesis of fluoro and trifluoromethyl substituents containing novel tetracyclic N-benzylated benzopiperazine fused acridone regioisomers using a greener solvent 2-MeTHF and their DFT studies. J. Fluor. Chem. 257–258, 109989 (2022).
Article Google Scholar
Veligeti, R., Anireddy, J. S., Madhu, R. B. & Ramakrishna, D. S. One pot, three component synthesis of fluoro and trifluoromethyl substituted unsymmetrical dihydropyrazine fused acridine-3-carboxamide using renewable 2-MeTHF solvent and their DFT studies. J. Fluor. Chem. 261–262, 110019 (2022).
Article Google Scholar
Frisch, M. J. et al. Fox (Gaussian Inc., Wallingford CT, 2013).
Google Scholar
Tatsuya, S., Ivana, K., Junui, N. & Nguyen, T. Solvent extraction of Zinc(II) with 1-Naphthoic acid into chloroform in the presence of Tetrabutylammonium ions or Trioctylphosphine oxide. Anal. Sci. 10, 743. https://doi.org/10.2116/analsci.10.743 (1994).
Article Google Scholar
Shawali, A. S., Elsheikh, S. & Párkányi, C. Cyclization of thiohydrazonate esters and Azo-Hydrazone Tautomerism of 2-Arylhydrazono-3-oxo-1, 4-benzothiazines. J. Heterocycl. Chem. 40, 207–212 (2003).
Article CAS Google Scholar
Kalarani, R., Sankarganesh, M., Kumar, G. G. V. & Kalanithi, M. Synthesis, spectral, DFT calculation, sensor, antimicrobial and DNA binding studies of Co(II), Cu(II) and Zn(II) metal complexes with 2-amino benzimidazole Schiff base. J. Mol. Struct. 1206, 127725 (2020).
Article CAS Google Scholar
Chong, J. et al. Experimental and theoretical studies on isatin-Schiff bases and their copper(II)-complexes: Syntheses, spectroscopy, tautomerism, redox potentials, EPR PXRD and DFT/TDDFT. J. Mol. Struct. 1201, 127725 (2020).
Google Scholar
Ramesh, G. et al. Facile synthesis, structural characterization, DNA binding, incision evaluation, antioxidant and antimicrobial activity studies of Cobalt (II), Nickle (II) and Copper (II) complexes of 3-amino-5-(4-fluorophenyl) isoxazole derivatives. J. Mol. Struct. 1202, 127338 (2020).
Article CAS Google Scholar
Zhang, F. et al. A Lanthanide MOF thin-film fixed with Co3O4 Nano-anchors as a highly efficient luminescent sensor for Nitrofuran antibiotics. Chem. Eur. J. 23, 10293–10300 (2017).
Article CAS PubMed Google Scholar
Lakshmi Praveen, P. & Durga, P. O. Photosensitivity, substituent and solvent-induced shifts in UV-visible absorption bands of naphthyl-ester liquid crystals: A comparative theoretical approach Liquid Crystals. Liq. Cryst. J. 41, 872–882 (2014).
Article Google Scholar
Lakshmi Praveen, P. Nematic and smectic bithiophenes for UV sensing mechanism: Comparative calculations on different homologues. J. Mol. Liq. 341, 117424 (2021).
Article CAS Google Scholar
Lakshmi Praveen, P., Ramakrishna, D. S. & Durga, P. O. UV spectral characterization of a smectic-C liquid crystal: Theoretical support to the experiment. J. Mol. Liq. 341, 117424 (2021).
Article CAS Google Scholar
Das, P. & Lakshmi Praveen, P. Theoretical investigation on absorption spectral profile of tetrazole liquid crystals: Hexyl, nonyl end groups and solvent effects. IOP Conf. Ser. Mater. Sci. Eng. 798, 012041. https://doi.org/10.1088/1757-899X/798/1/012041 (2020).
Article CAS Google Scholar
Shoba, D., Periandy, S., Karabacak, M. & Ramalingam, S. Vibrational spectroscopy (FT-IR and FT-Raman) investigation and hybrid computational (HF and DFT) analysis on the structure of 2, 3-naphthalenediol. Spectrochim. Acta Part A Mol. Biomol. Spectrosc. 83, 540–552 (2011).
Article ADS CAS Google Scholar
Fukui, K. Role of frontier orbitals in chemical reactions. Sci. 218, 747–754 (1982).
Article ADS CAS Google Scholar
Koopmans, T. On the assignment of wave functions and eigenvalues to the individual electrons of an atom. Physica. 1, 104–113 (1934).
Article ADS Google Scholar
Pearson, R. G. Absolute electronegativity and absolute hardness of Lewis acids and bases. J. Am. Chem. Soc. 107, 6801–6806 (1985).
Article CAS Google Scholar
Pearson, R. G. The principle of maximum hardness: chemical hardness. J. Chem. Ed. 76, 267 (1999).
Article CAS Google Scholar
Reed, A. E., Curtiss, L. A. & Weinhold, F. Intermolecular Interactions from a Natural Bond Orbital. Donor-Accept. Viewp. Chem. Revs. 88, 899-926I (1988).
Article CAS Google Scholar
Ebenso, E. et al. Theoretical studies of some sulphonamides as corrosion inhibitors for mild steel in acidic medium. J. Quantum Chem. 110, 2614 (2010).
Article CAS Google Scholar
Parr, R. G., Donnelly, R. A., Levy, M. & Palke, W. E. Electronegativity : Density functional viewpoint. J. Chem. Phys. 68, 3801–3807 (1978).
Article ADS CAS Google Scholar
Han, Q. et al. Determination of palladium in water samples using cloud point extraction coupled with laser thermal lens spectrometry. J. Korean Chem. Soc. 59, 407–412 (2015).
Article CAS Google Scholar
Shrivastava, A. & Gupta, V. Methods for the determination of limit of detection and limit of quantitation of the analytical methods. Chron. Young Sci. 2, 21 (2011).
Article Google Scholar
Doyle, F. M. Ion flotation—Its potential for hydrometallurgical operations. Int. J. Miner. Process. 72, 387–399 (2003).
Article CAS Google Scholar
Tavakoli, L. et al. Development of cloud point extraction for simultaneous extraction and determination of gold and palladium using ICP-OES. J. Hazard. Mater. 152, 737–743 (2008).
Article CAS PubMed Google Scholar
Behbahani, M. et al. Solid phase extraction using nanoporous MCM-41 modified with 3,4-dihydroxybenzaldehyde for simultaneous preconcentration and removal of gold (III), palladium (II), copper (II) and silver (I). J. Ind. Eng. Chem. 20, 2248–2255 (2014).
Article CAS Google Scholar
Ghaedi, M., Ghayedi, M., Kokhdan, S. N., Sahraei, R. & Daneshfar, A. Palladium, silver, and zinc oxide nanoparticles loaded on activated carbon as adsorbent for removal of bromophenol red from aqueous solution. J. Ind. Eng. Chem. 19, 1209–1217 (2013).
Article CAS Google Scholar
Zhang, S., Pu, Q., Liu, P., Sun, Q. & Su, Z. Synthesis of amidinothioureido-silica gel and its application to flame atomic absorption spectrometric determination of silver, gold and palladium with on-line preconcentration and separation. Anal. Chim. Acta 452, 223–230 (2002).
Article CAS Google Scholar
Liang, P., Zhao, E., Ding, Q. & Du, D. Multiwalled carbon nanotubes microcolumn preconcentration and determination of gold in geological and water samples by flame atomic absorption spectrometry. Spectrochim. Acta Part B At. Spectrosc. 63, 714–717 (2008).
Article ADS Google Scholar
Ashkenani, H. & Taher, M. A. Use of ionic liquid in simultaneous microextraction procedure for determination of gold and silver by ETAAS. Microchem. J. 103, 185–190 (2012).
Article CAS Google Scholar
Ebrahimzadeh, H., Tavassoli, N., Amini, M. M., Fazaeli, Y. & Abedi, H. Determination of very low levels of gold and palladium in wastewater and soil samples by atomic absorption after preconcentration on modified MCM-48 and MCM-41 silica. Talanta 81, 1183 (2010).
Article CAS PubMed Google Scholar
Ebrahimzadeh, H., Moazzen, E., Amini, M. M. & Sadeghi, O. Novel ion imprinted polymer coated multiwalled carbon nanotubes as a high selective sorbent for determination of gold ions in environmental samples. Chem. Eng. J. 215–216, 315–321 (2013).
Article Google Scholar
Shamsipur, M. & Ramezani, M. Selective determination of ultra-trace amounts of gold by graphite furnace atomic absorption spectrometry after dispersive liquid-liquid microextraction. Talanta 75, 294–300 (2008).
Article CAS PubMed Google Scholar
Download references
Open access funding provided by The Science, Technology & Innovation Funding Authority (STDF) in cooperation with The Egyptian Knowledge Bank (EKB).
Chemistry Department, Faculty of Science, Mansoura University, Mansoura, 35516, Egypt
Magda A. Akl, Nora A. El-Mahdy & El-Sayed R. H. El-Gharkawy
You can also search for this author in PubMed Google Scholar
You can also search for this author in PubMed Google Scholar
You can also search for this author in PubMed Google Scholar
Authorship contribution statement. Magda A. Akl: Conceptualization, Methodology, Investigation, Writing—original draft, review, Supervision. Nora A.El-Mahdy.: Methodology, Investigation, Writing—original draft. El-Sayed.R.H.El–Gharkawy.: Conceptualization, Methodology, Investigation, Writing—original draft.
Correspondence to Magda A. Akl.
The authors declare no competing interests.
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.
Reprints and Permissions
Akl, M.A., El-Mahdy, N.A. & El-Gharkawy, ES.R.H. Design, structural, spectral, DFT and analytical studies of novel nano-palladium schiff base complex. Sci Rep 12, 17451 (2022). https://doi.org/10.1038/s41598-022-21406-x
Download citation
Received: 04 July 2022
Accepted: 27 September 2022
Published: 19 October 2022
DOI: https://doi.org/10.1038/s41598-022-21406-x
Anyone you share the following link with will be able to read this content:
Sorry, a shareable link is not currently available for this article.
Provided by the Springer Nature SharedIt content-sharing initiative
By submitting a comment you agree to abide by our Terms and Community Guidelines. If you find something abusive or that does not comply with our terms or guidelines please flag it as inappropriate.