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Lanthanum(III) potentiometric sensors based on ethyl benzoyl acetate
⁎Corresponding author. e_uossry@yahoo.com (Eman Y.Z. Frag)
-
Received: ,
Accepted: ,
This article was originally published by Elsevier and was migrated to Scientific Scholar after the change of Publisher.
Abstract
Modified carbon paste electrode (CPE) and screen printed electrode (SPE) based on ethyl benzoyl acetate (EBA) were prepared and investigated as lanthanum ion selective electrodes. Effect of various plasticizers (o-NPOE, TCP, DBP, DOS, and DOP) and ionophore content was studied. The reaction mechanism between La(III) and β-diketone ionophore at the electrode surface was studied through scanning electron microscopy (SEM), energy dispersive X-ray analysis (EDX) and IR spectra measurement. The best performance was obtained using modified SPE and CPE electrodes with o-NPOE and TCP plasticizers. These electrodes showed potentiometric response with a Nernstian slope of 21.0, 19.5 and 20.5 mV decade−1 over a concentration range from 1.0 × 10−6 to 1.0 × 10−2 mol L−1 with a fast response time of 9, 10 and 13 s over the linear concentration range for modified SPE (electrode I; TCP plasticizer) and two modified CPE plasticized with o-NPOE (electrode II) and TCP (electrode III), respectively. The electrodes exhibited constant potentiometric response in pH range 4–8, 5–8 and 4–7 for electrodes I, II and III, respectively. They showed satisfactory good sensitivity toward lanthanum ions with regard to most common transition metal ions. The sensors were applied for determination of La(III) ion in different water samples (tap water and wastewater) with satisfactory and good reproducibility results.
Keywords
SPE
CPE
Lanthanum(III)
β-diketone
SEM
EDX
1 Introduction
Lanthanides were considered due to the unique physical and chemical properties of the rare earth elements (REEs). Lanthanides were used widely in metallurgy, medicine, chemical engineering, electronics and electrooptics, biomedicine, for manufacturing of magnetostriction materials, lasers, storage batteries with long service life for electric vehicles, etc. (Tadjarodi et al., 2015). Lanthanum was one of lanthanide elements found in rare earth minerals such as cerite, monazite, allanite and bastnasite (Khan et al., 2014). Lanthanum(III) was considered as fission products. It may be leaked to the environment and cause risks. So they were considered as hazardous materials (Besharati-Seidani and Shamsipur, 2015). The lanthanum alloy LaCo5 was used as a permanent magnet and LaNi5 for hydrogen storage. Its high index of refraction made very pure La2O3 a useful additive to optical glass for camera lenses (Singh et al., 2012).
Because of the discharge of lanthanum ions in the environment and its useful and harmful biological activity, the La(III) ion determination was carried out using different analytical methods. These methods included flame photometry, atomic absorption spectrometry, inductively coupled plasma-mass spectrometry (ICP-MS) Islamnezhad et al. (2011), ion chromatography (Al-Shawi and Dahl, 1996), atomic emission spectrometry (Jia et al., 2008), inductively coupled plasma-optical emission spectrometry (ICP-OES) Waqar et al. (2009), sector field inductively coupled plasma mass spectrometry (Chung, 2009) and electrothermal vaporization inductively coupled plasma mass spectrometry (Zhang et al., 2007), etc.
During last two decades, a general interest in metal β-diketonates (Mehrotra et al., 1978) was reflected in the chemistry of lanthanides. This resulted in detailed investigation unfolding some lesser known facts of general lanthanide coordination chemistry. Early methods used for preparation of lanthanide tris-β-diketonates were examined previously (Moeller et al., 1961). It was established that the products from aqueous solutions were invariably hydrates while sometimes hydroxy derivatives were also formed. A large number of β-diketonates of lanthanides were prepared (Dutt et al., 1971; Dutt and Rahut, 1971; Dutt and Samyal, 1971; Stites et al., 1948).
One of the most important analytical techniques capable of determining both organic and inorganic materials in medico-biological practice (Mohamed et al., 2013) was ion selective electrodes (ISE). There was a constant progress in the number of electrodes capable of selectively determining large numbers of metal ions such as carbon paste electrodes (CPEs). Although the CPEs had an important role in the electrochemical analysis, the prepared pastes were soft, non-compactable and had to be packed into a special piston shaped holder. However, in the case of determinations in flowing streams or field monitoring with portable analyzers, the shapes and designs of such sensors were not suitable for every purpose as where the respective detection units need sensors of special characters (Svancara et al., 2005).
While screen printing electrodes were reproducible, inexpensive and sensitive disposable electrochemical electrodes were used for the determination of trace levels of substances in environmental, pharmaceutical and biomedical samples (Fanjul-Bolado et al., 2008).
The use of modified chemical sensors in determination of metal ions was developed in recent years as they provide fast, accurate, sensitive, reliable and low cost method rather than the methods mentioned before. So the aim of the present paper was to fabricate modified screen printed electrode (electrode I) and carbon paste electrodes (II and III) with ethyl benzoyl acetate (EBA) as electroactive material for selective determination of lanthanum (III) ion in different water samples.
The type and content of ionophore, suitable pH, plasticizer type, effect of interfering ions and temperature effect on the performance of the electrodes were also studied. The reaction mechanism at the electrode surface was studied using IR spectra. The change in the electrode surface as the results of complex formation between EBA ionophore and La(III) ion was studied using SEM, EDX and IR spectra. The method was successfully applied for determination of lanthanum(III) ion in different real water samples using spiking technique. Method validation parameters were optimized according to ICH guidelines and the proposed potentiometric method can be applied successfully for the determination of La(III) ions in routine samples.
2 Experimental
2.1 Materials
Reagent grade acetyl acetone (AA), β-diketone 1-benzoyl-2-nonanone (Lix 54), ethylacetoacetate (EAA), and ethyl benzoyl acetate (EBA) were supplied from Aldrich as electroactive materials. Lanthanum chloride was supplied from Aldrich. Graphite fine powder (extra pure) was of analytical grade and purchased from Merck. High molecular weight polyvinyl chloride (PVC) powder was supplied from Aldrich, while o-nitrophenyl octyl ether (o-NPOE) was supplied from Fluka. Dioctylphthalate (DOP), tricresyl phosphate (TCP), dibutyl phthalate (DBP) and dioctylsebacate (DOS) were supplied from BDH. Acetone and cyclohexanone were supplied from Fluka (Switzerland).
2.2 Apparatus and emf measurements
Digital Hanna pH/mV meter (model 8417) was used for all potentiometric measurements at 25 °C. Spectrophotometer (U-2001, model 121-0032 Hitachi, Tokyo, Japan) and scanning electron microscope (National Research Center Quanta FEG250) were used and microanalysis was completed using the energy dispersive X-ray analyzer (EDX) (National research center, Egypt). FT-IR spectra were recorded on a Perkin-Elmer 1650 spectrometer (4000–400 cm−1) in KBr pellets at the Microanalytical Center, Cairo University, Egypt. Ag/AgCl reference electrode contains 10% (w/v) potassium chloride.
2.3 Sensors preparation (screen printed and carbon paste)
CPEs were prepared using Teflon holder for carbon paste filling as the electrode body, and the carbon paste was formed by mixing graphite powder (250 mg), a suitable liquid binder (DOP, TCP, DBP, DOS or o-NPOE) (100 μL) and 2.5–12.5 mg of ionophore. This matrix was thoroughly mixed in the mortar and the resulted paste was used to fill the electrode body. A new carbon-paste surface was obtained by pushing gently the stainless-steel screw forward.
SPEs were printed in arrays of six couples consisting of the working electrodes (each 5 × 35 mm) following the procedures previously described (Nour El-Dien et al., 2012; Frag et al., 2011a–c, 2012; Akl et al., 2013; Mohamed et al., 2010). A polyvinyl chloride flexible sheet (0.2 mm) was used as a substrate which was not affected by the curing temperature or the ink solvent and easily cut by scissors. The working electrodes were printed using homemade carbon ink (prepared by mixing 1–15 mg of EBA electroactive material, 450 mg TCP, 1.25 g of polyvinyl chloride (8% w v) and 0.75 g carbon powder). They were printed and cured at 50 °C for 2 h. A layer of an insulator was then placed onto the printed electrodes, leaving a defined rectangular shaped (5 × 5 mm) working area and a similar area (for the electrical contact) on the other side. Fabricated electrodes were stored at 4 °C and used directly in the potentiometric measurements without any preconditioning.
2.4 EMF measurements
The emf measurement with the plasticized SPE and CPEs was carried out with the following cell assemblies:
The detection limit was taken at the point of intersection of the extrapolated linear segments of the calibration curve which was plotted with emf as a function of the negative logarithm of lanthanum ion concentration, and the selectivity of the electrodes is obtained by measuring the selectivity coefficient (KpotLa,J) using the separate solution method using 0.001 mol L−1 La(III) and interfering ions.
2.5 Determination of La(III) ion in different water samples
Tap water and wastewater samples were collected from different environment filtered and analyzed for La(III) ion by the proposed method. Tap water (sample 1) and wastewater (sample 2) samples were supplied from Sandoub, Mansoura, Dakahliya, Egypt.
The water samples were spiked with known amounts of lanthanum(III) ion, the pH was adjusted with acetate buffer (pH = 4) and they were analyzed by the proposed general procedure.
For spectrophotometric measurements at 430 nm a given amount of alizarin Red S was added to 5 beakers containing 10 ml spiked water samples with acetate buffer solution and the pH of the solution was adjusted to 4.60 with hydrochloric acid or sodium hydroxide and then diluted to 50 ml. This was followed by absorbance measurements. The molecular ratio of lanthanum:alizarin Red S is 1:2 (Kawashima et al., 1961).
2.6 Surface analysis
Scanning electron microscope (SEM) and energy dispersive X-ray (EDX) analyzer were used for morphological analysis of the sensors surface at 4000× magnifications for electrodes I and III before and after the interaction with lanthanum (III) ion.
3 Result and discussion
3.1 Electrode composition
3.1.1 Type of ionophore
An important requirement for the preparation of an ion selective sensor was the electroactive material (ionophore), which was used in the paste. It should exhibit high lipophilicity and strong affinity for a particular ion to be determined and poor affinity for others. They should have rapid exchange kinetics and adequate complex formation constants in the paste and should be well soluble in the paste matrix. It should have a sufficient lipophilicity to prevent leaching from the paste into the sample solution.
The lanthanum ion showed high affinity toward β-diketone compounds due to the higher oxidation-reduction potential, higher bond energy with oxygen and larger atomic radius (Bian et al., 2006). Different β-diketone compounds namely acetyl acetone (AA), Lix 54, ethyl acetoacetate (EAA), and ethyl benzoyl acetate (EBA) were used to study the selectivity toward lanthanum(III) ion showing potentiometric response with slope values of 23.0, 18.0, 12.5 and 19.9 mV decade−1, respectively. It was obvious that the EBA ionophore was the best electroactive material toward lanthanum(III) ion since it gave the best slope within the studied concentration range.
3.1.2 Ionophore content
Different amounts of EBA ionophore as electroactive material were used to prepare the modified SPE and CPEs for La(III) ion determination. The potential response is shown in Figs. 1 and 2 for modified SPE and CPEs electrodes, respectively.
Effect of ionophore content on potential response of SPE (electrode I) for determination of La(III) in acetate buffer (pH = 4).

Effect of ionophore content on potential response of CPE (electrode III) for determination of La(III) in acetate buffer (pH = 4).
It was found from the figures that the sensors modified with 2.5 mg and 10 mg of EBA ionophore which was the most effective amount gave the best sensitivity with the best Nernstian slope of 21.0, 19.9 and 20.5 mV decade−1, over a wide concentration range from 1.0 × 10−6 to 1.0 × 10−2 mol L−1 with a good correlation coefficient and very low detection limit for electrodes I, II and III, respectively. The limits of detection were determined from the intersection of the two extrapolated segments of the calibration plots and were found to be 1.0 × 10−6 mol L−1.
3.1.3 Effect of plasticizers type in CPE
The nature of plasticizer was expected to play a key role in determining the ion-selective characteristics as it influences the dielectric constant of the paste of the electrode, the mobility of the ionophore molecule and state of ligand (Gupta et al., 2003). It also caused selective extraction of the target ion which created the electrochemical phase boundary potential due to thermodynamic equilibria at the interface. So, various plasticizers were used namely DBP, DOP, o-NPOE, DOS and TCP in order to study their influence on the performance of the sensors.
Among these plasticizers, o-NPOE and TCP provided faster, more stable and sensitive response in the concentration range from 1.0 × 10−6 to 1.0 × 10−2 mol L−1 as shown from the graph. The slope was 19.9 and 20.5 mV per decade for CPE electrodes II and III, respectively. This can be explained due to its high dielectric constant and relatively high molecular weight.
According to the Lubricating Theory of plasticization (Wilkes et al., 2005), the plasticizer molecules diffuse into the polymer and act as shields to reduce polymer–polymer interactive forces (van der Waals forces) and hence prevent the formation of a rigid network. This lowers the PVC Tg and allows the polymer chains to move rapidly each other, resulting in increased flexibility, softness, and elongation. Different plasticizers yield different plasticization effects because of the differences in the strengths of the plasticizer–polymer and plasticizer–plasticizer interactions. At low plasticizer levels, the plasticizer–PVC interactions were the dominant interactions, while plasticizer–plasticizer interactions can become more significant at high plasticizer concentrations. The polar portion of the molecule must be able to bind reversibly with the PVC polymer, thus softening the PVC, while the non-polar portion of the molecule allows the PVC interaction to be controlled so it is not so powerful a solvator as to destroy the PVC crystallinity.
3.1.4 Surface characterization
In order to characterize the morphology of the CPE and SPE, scanning electron microscopy (SEM) and energy dispersive X-ray (EDX) analyzer were used as shown in Figs. 3–6. All electrodes surfaces showed a similar configuration with randomly directed graphite particles ensemble into an insulator matrix (PVC or plasticizer for SPE and CPE, respectively) where the graphite particle size is longer for CPE than for SPE, so this distribution of the electrode material in case of SPE (microelectrodes) could lead to a highly packed structure. SPE showed a more uniform surface topography rather than CPE. Incorporation of a suitable ionophore in the paste followed by soaking of the sensors in La(III) ion solution led to the complex formation between the La(III) ions and EBA ionophore which was observed in filling the space between graphite surface after the interaction with La(III) ion. Formation of ionophore-La3+ complex at electrode surface which was subsequently extracted by the plasticizer into the paste is shown in Figs. 4 and 6. These data are supported by IR spectra as shown in Figs. 7 and 8, where the ligand EBA exhibited medium intensity bands at 1740 and 1685 cm−1 due to υ(C⚌O) of benzoyl and ester groups for electrodes I and III, respectively. After soaking electrodes I and III in La(III) ion solution for 1 h and carrying out IR spectra, a difference in the spectra is observed. The bands due to υ(C⚌O) of benzoyl and ester groups were shifted to lower wave numbers in the spectrum (1729 and 1644 for electrode I and 1741 and 1613 cm−1 for electrode III) suggesting complex formation via coordination of the EBA ionophore to La(III) ion through the C⚌O of benzoyl and C⚌O of ester groups .
SEM images for SPE surface, electrode I (a) before and (b) after soaking in 1 × 10−3 mol L−1 La(III) ion.

EDX of SPE surface, electrode I (a) before and (b) after soaking in 1.0 × 10−3 mol L−1 La(III) ion.

SEM images for CPE surface, electrode III (a) before and (b) after soaking in 1 × 10−3 mol L−1 La(III) ion.

EDX of CPE surface, electrode III (a) before and (b) after soaking in 1.0 × 10−3 mol L−1 La(III) ion.

IR spectra for electrode III (a) before and (b) after soaking in 1.0 × 10−3 mol L−1 La(III) ion.

IR spectra for electrode I (a) before and (b) after soaking in 1.0 × 10−3 mol L−1 La(III) ion.
3.2 The effect of pH
The pH dependence of the electrode potential was investigated over the pH range of 2.0–10.0 in a 1.0 × 10−3 and 1.0 × 10−5 mol L−1 solution of La(III) ion. The pH was adjusted by using very small volumes of HCl and NaOH solutions. The results indicated that the potential was independent of pH in the range of 4–8, 5–8 and 4–7 for electrodes I, II and III, respectively. Outside this range, the potential changed significantly. The increase of potential below pH 4.0 may be ascribed to the competitive binding of protons to the ligands on the electrode surface rather than La(III) ion. The decrease of potential above pH 8.0 can be accounted for to the formation of hydroxyl complexes of La(III) such as La(OH)+2, La(OH)2+ and La(OH)3 which monished its ability to combine with the carrier (Yuan et al., 2013; Shamsipur et al., 2002).
3.3 Response time
The time it takes for the electrode potential of an ion selective electrode to become stable within a range of variation of ±1 mV depends on electrode type and structure, ion type, concentration, and ionic strength. The response time when measuring a high ion concentration after measuring low ion concentrations was relatively short, while a longer response time was obtained for the reverse process. Additionally, at around the minimum measurement limit, the response time was generally relatively long, being of the order of several minutes. Hence, when using the ion electrode method, it was necessary to wait until the potentiometer indicated a stable value before taking a reading (Eric et al., 1997).
One of the most important factors for any ion-selective electrode is response time. The practical response time of the sensor was recorded by observing the potential change over a concentration range from 1.0 × 10−6 to 1.0 × 10−2 mol L−1 of La(III). The potentials versus time traces are shown in Fig. 9.
Dynamic response time of (a) electrode I, (b) electrode II and (c) electrode III for La(III) in acetate buffer (pH = 4).
As can be shown in Fig. 9, electrodes reached their equilibrium responses in a very short time of 9, 10 and 13 s over the linear concentration range for electrodes I, II and III, respectively. This may be due to the fast exchange kinetics of complexation–decomplexation of La(III) ion with the ionophore at the paste of the electrodes (Ganjali et al., 2004).
3.4 Effect of temperature
One of the important parameters which has effect on the performance of the sensors is the change of temperature at test solution. The stability of the electrodes was studied within the temperatures 10, 20, 30, 40, 50 and 60 °C. The electrode exhibited good Nernstian behavior in the temperature range (10–50 °C). The slope of electrode did not show a good Nernstian behavior at higher temperature. The standard cell potentials (E°Cell), were determined at different temperatures from the respective calibration plots as the intercepts of these plots at p La(III) = 0, and were used to determine the isothermal temperature coefficient (dE0/dt) of the cell with the aid of the following equation (Khalil and El-Aliem, 2002; Electrochemistry, 1972):
Plot of E0 electrode versus (t–25) gave a straight line. The slope of the line was taken as the isothermal temperature coefficient of the La (III) electrode. It amounted to 0.121 × 10−2, 0.55 × 10−3 and 0.245 × 10−2 V/°C for electrodes I, II and III, respectively. The small values of (dE0/dt)cell and (dE0/dt)electrode revealed the high thermal stability of the electrodes within the investigated temperature range.
3.5 Selectivity
Clearly, the selectivity was one of the most important characteristics of a sensor. It often determines whether a reliable measurement in the target sample was possible or not. In clinical applications, it was critical where the allowed emf deviation (error) may sometimes not be larger than 0.1 mV for whole blood or serum measurements. Theoretically, selectivity description allowed researchers to identify the key parameters for optimizing the performance of potentiometric sensors, e.g., by adjusting weighing parameters (i.e., absolute membrane concentrations) or choosing different plasticizers or matrices (Eric et al., 1997). Ion selective electrodes have the most important characteristic that is its relative response to other ions present in solution, which expressed in terms of selectivity coefficients (KA,BPot). Different methods can be used for measuring the selectivity coefficients of the electrode such as separate solution method (SSM) Bakker et al. (2000) and matched potential method (MPM) Lindner and Umezawa (2008). In the present study SSM was used which depends on measuring the potential of a cell comprising an ISE and a reference electrode with two separate solutions. One contains the ion of interest A at the activity aA (but no B) and the other contains the interfering ion B at the same activity aB = aA (but no A). In this method, the values of the selectivity coefficient can be derived from the following equation: EA and EB mean the potentiometric response of aA and aB, respectively. aA is the primary ion activity and aB is the activity of an interfering ion. The single ion activities were calculated by the extended Debye-Hückel equation (Kamata et al., 1998).
In this work, aA (1.0 × 10−3 mol L−1 La(III) ion) and aB (1.0 × 10−3 mol L−1 interfering ion) were used to measure the selectivity coefficients. S, Nernstian slope, ZA and ZB are the charge of the primary and interfering ions, respectively. The selectivity coefficient values are listed in Table 1. The value of selectivity coefficient reached to 1.0 indicated equal response to both primary ion and interfering ions. If the value of selectivity coefficient was smaller than 1.0, it showed that the sensor was selective to the primary ion over the interfering ions. The data given in Table 1 indicate that the electrodes (I and III) have good selectivity toward the lanthanum ion than other metal ions. But for electrode II, it had good selectivity toward primary lanthanum ion except in the presence of Al(III), Ca(II) and Mg(II) ions, and it showed interfering ion with those metal ions.
SPE Electrode I (2.5 mg EBA)
CPE
Electrode II
Electrode III
Interfering Species
Log KpotLa3+,B
Log KpotLa3+,B
Log KpotLa3+,B
Fe3+
−11
−16
−21
Mn2+
−9.7
−10
−5.7
Sr2+
−9.61
−9
−5.8
Na+
−13.43
–
–
Ce3+
–
−16
−15
Ni2+
−9.07
−10.1
−4.7
Co2+
−8.64
−7.6
−6.8
Pb2+
−10.78
−9.1
−7.6
Zn2+
−8.40
−2.4
−5.4
Fe2+
−10.07
−3.2
−6
K+
−11.33
−10
−9
Ba2+
−8.73
−3.8
−7.2
Cd2+
−9.40
−4.2
−5.3
Cr3+
−9.40
−6.05
−8.6
Mg2+
−7.97
−2.5
−5
Al3+
−7.62
−2.7
−7.7
Cu2+
−10.07
−4
−10
Ca2+
−7.02
−2.9
−4.7
Zr4+
−10.01
–
–
V5+
−5.28
–
–
3.6 Life time
Electrodes (I–III) were tested at different intervals to follow up its life time and reproducibility. It was clear from the figure that modified SPE had the longest life time up to three weeks.
The surface of CPEs was continuously polished using a filter paper during calibration process to obtain new working surface and rinsed carefully with double distilled water to remove the memory effect of electrode. This indicated that the SPE had high mechanical durability and good adherent properties. Longer stability test was also investigated and the electrodes were successfully used for at least 50 consecutive measurements without any preconditioning before use.
3.7 Analytical application
In general, the maximum La(III) ion concentration that ion selective electrodes can measure was found to be 1.0 × 10−2 mol L−1, and the minimum was 1.0 × 10−6 mol L−1. The proposed Lanthanum ion-selective electrodes (I-III) were used for potentiometric determination of lanthanum(III) ion in different water samples (waste and tape water). As mentioned above in procedure (2.7) the samples were treated and analyzed. The results obtained were also compared with those from spectrophotometric analysis. The results obtained and listed in Table 2 indicated the successful use of the proposed electrodes (I-III) for determination of lanthanum ion and there was a satisfactory agreement with those obtained by spectrophotometric method.
Sample
Taken (mg mL−1)
Spectrophotometry
Electrode II
Electrode III
Electrode I
Found (mg mL−1)
% Recovery
Found (mg mL−1)
% Recovery
Found (mg mL−1)
% Recovery
Found (mg mL−1)
% Recovery
2
3.22
3.22
100.0
3.16
98.13%
3.14
97.52%
3.21
99.69%
2
1.611
1.67
103.6
1.59
98.69%
1.68
104.28%
1.611
100.0%
1
0.322
0.33
102.4
0.322
100.0%
0.322
100.0%
0.331
102.79%
1
1.611
1.66
103.0
1.58
98.08%
1.69
104.90%
1.585
98.39%
3.8 Method validation
3.8.1 Inter- and intra-day accuracy and precision
Different real water samples spiked with different concentrations of La(III) ion were used to carry out four replicate experiments to evaluate the validity and applicability of the proposed method and reproducibility of the results obtained. Tables 3 and 4 show the values of the inter- and intra-day relative standard deviations for different concentrations of the samples, obtained from experiments carried out over a period of four days (inter-day) or within the same day (intra-day). It was found that, modified SPE had reproducible response in the intra-day measurements rather than modified CPE which need to scratch the paste surface to remove the memory effect and obtain a new surface electrode and this is considered an advantage of SPE over CPE. From the data obtained, the relative standard deviations were found to be small indicating reasonable repeatability of the proposed sensors, so modified CPEs and SPE were successfully applied to determine La(III) in pure and wastewater samples.
Taken, mg mL−1
Found, mg mL−1
Recovery %
SD
RSD %
Inter day
Intra day
Inter day
Intra day
Inter day
Intra day
Inter day
Intra day
Pure
3.249
3.235
3.216
99.57
98.90
1.270
0.577
1.29
0.542
0.325
0.318
0.322
97.80
99.00
0.350
0.955
0.359
0.793
0.033
0.033
0.032
100.0
96.90
0.411
0.478
3.87
0.367
Water sample No. 1
0.322
0.322
0.331
100.0
102.8
0.478
0.478
4.012
1.239
1.611
1.600
1.585
99.32
98.39
0.500
0.500
5.714
0.836
Water sample No. 2
3.220
3.190
3.210
99.07
99.69
0.500
0.478
6.800
0.644
1.611
1.609
1.611
99.88
100.0
0.478
0.500
6.490
1.290
Taken, mg mL−1
Found, mg mL−1
Recovery %
SD
RSD %
Electrode II
Electrode III
Electrode II
Electrode III
Electrode II
Electrode III
Electrode II
Electrode III
Pure
0.325
0.321
0.316
98.70
97.23
0.500
0.157
1.526
3.125
0.033
0.032
0.032
98.00
96.97
0.478
0.479
2.139
0.450
Water sample No. 1
0.322
0.317
0.322
98.44
100.0
0.816
0.525
2.148
0.416
1.611
1.610
1.690
99.90
104.9
0.500
0.816
6.870
0.703
Water sample No. 2
3.220
3.160
3.270
98.14
101.55
0.478
0.816
7.509
0.595
1.611
1.611
1.680
100.0
104.28
0.577
0.645
0.289
0.431
3.8.2 Limits of detection and quantification
The limit of quantification (LOQ) was determined by establishing the least concentration that can be measured according to ICH Q2(R1) recommendations, below which the calibration range was non linear. The results obtained are listed in Table 5. The limit of detection (LOD) was determined by evaluating the lowest concentration of the measuring ions analytes that can be readily detected and were found to be 1.0 × 10−6 mol L−1. The LOQ and LOD were calculated according to the following equations (ICH 2005):
where (Sa) is the standard deviation of the intercept of the regression line and (b) is the slope of the calibration curve.
Parameters
Electrode I
Electrode II
Electrode III
Slope, mV decade−1
21.0
20.5
19.5
Linear range, mol L−1
1.0 × 10−6–1.0 × 10−2
1.0 × 10−6–1.0 × 10−2
1.0 × 10−6–1.0 × 10−2
Limit of detection, mol L−1
1.0 × 10−6
1.0 × 10−6
1.0 × 10−6
Limit of quantification, mol L−1
3.3 × 10−6
3.3 × 10−6
3.3 × 10−6
Working pH range,
4–8
5–8
4–7
Life time, days
25
8
8
SD
0.879
0.288
0.894
RSD
0.998
0.962
0.999
Intercept
176
199.6
204
Recovery %
101
99.0
100
Isothermal coefficient V/°C
0.121 × 10−2
0.55× 10−3
0.2450−2
3.8.3 Linearity
The calibration graphs obtained by plotting the potential values versus the final concentration were found to be rectilinear over the concentration range cited in Table 5.
4 Conclusion
In this work, modified ion selective electrodes (carbon paste and screen printed) were fabricated based on EBA as ionophore. The proposed electrodes possessed excellent performance in determination of La(III) in tap water and wastewater with high recovery in comparison with spectrophotometric method with high sensitivity, good selectivity, fast response, and low detection limit with Nernstian behavior over a wide concentration range.
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