Sensor for Silver (I) Ion Based on Schiff-base-N, N’ [1, 1’-dithiobis (phenyl)] bis (5’methoxysalicyl-aldimine) (5-MeOSalps)
Geetu Bansal1* and Susheel Kumar Sindhu2
1Department of Chemistry, Guru Premsukh Memorial College of Engineering 245, G.T. Karnal Road, Budhpur, Delhi-110 036
2Department of Chemistry, S.S.V. P.G. College, Hapur
*Corresponding Author E-mail: geetukuchhal@gmail.com
ABSTRACT:
The preparation of silver ion selective polymer membrane and its application to ion selective electrode is reported here. PVC membrane contains silver selective N, N’ [1, 1’-dithiobis (phenyl)]bis(5’methoxysalicyl-aldimine) (5-MeOSalps) as ionophore. The sensor possess a nernstian slope of 58.20 ± 0.5 mV per decade over a wide linear concentration of 1.0 × 10-1 to1.0 × 10-6 M with a detection limit of 5.0 × 10-6 M. The electrode response is stable over wide pH range of 4.5 -10.5. It has a fast response time of 5 s and can be used for more than 5 min. without any considerable change in potential. The proposed electrode shows good selectivity over a variety of alkali, alkaline earth and transition metal ions.
Amongst the various analytical techniques available, use of ion selective membrane electrode is well established routine analytical technique. Advances in analytical industry in terms of better selectivity, fast response and long life has prompted a new search for better ionophores possessing electrical neutrality, lipophilic character, capability to select and reversibly bind metal ions to induce a selective permeation of metal ions through the membrane electrode1-3. In the past extensive methods have been made to improve the selectivity of Ag+ ion selective electrode. Thus, many cyclic and cyclic macromolecule have been suggested as electroactive ionophores e.g. non-macrocyclic compounds4-9, macrocyclic molecule compounds10, polyamine11 and metalloporphyrin12. The present paper deals with schiff base 5-MeOSalps based ISE for determination of Ag+. The Ag+ selectivity may be due to the electrostatic interaction between the metal ion, the aza crown cavity and the Schiff base. This sensor has been proved to be superior compared to some of those electrodes reported earlier in terms of a wide concentration range, better response time and longer life span.
Because Macromolecule ligands form selective and stable complexes with the metal ion of compatible dimension13 and can potentially be applied to their selective separation and determination14, continuous interest has been focused on the design and synthesis of new functionalized macro molecules for specific applications15.
EXPERIMENTAL:
REAGENTS AND CHEMICALS:
All reagents used in this were of analytical reagent grade. Most of the salts were purchased from E. Merck and were used as received. High molecular PVC powder and diamines like o-phenylenediamine, 2,6-diaminopyridine was purchased from Sigma Aldrich. Glyoxyl (40% aqueous solution), benzyl, semi-carbazide hydrochloride were purchased from CDH. Various plasticizers like benzyl acetate (BA), tetrakis- (4-chloro phenyl borate) (KTK) were taken from Fluka and 2-nitrophenyloctylether (o-NPOE) and sodium tetra phenyl borate (NaTPB) used were from Merck. Triply distilled water was used throughout. Ethanol was refluxed and distilled over lime before use.
SYNTHESIS OF ELECTROACTIVE MATERIAL:16
A solution of 5-methoxysalicylaldehyde (2.45 g, 16.1mmol.) in ethanol (10ml) was added to a solution of 2-aminophenyldisulphide (2.00 g, 8.05 mmol) in ethanol (50 ml) with stirring. The mixture was refluxed for 2 hrs. and the yellow precipitates of 5-MeOSalps was filtered off and recrystallised from chloroform/ethanol (94%).
Fig. 1 Structure of N.N’[1,1’dithiobis(phenyl)]bis(5’-methoxysalicyl-aldimine) (5-MeOSalps)
ELECTRODE PREPARATION:17
The solution of PVC membrane was prepared by thorough mixing of ionophore (Schiff base legend) (1% wt.), DBP (dibutylphthalate) as plasticizer (66% wt.) and PVC (33% wt.) and was dissolved in THF. The resulting solution was poured into a glass mould and THF was allowed to evaporate off at room temperature for 24 hrs. A flexible membrane of the thickness of 0.2-0.4 mm was obtained. The disc of 6mm diameter was cut and pasted onto the glass tube with PVC glue and conditioned with AgNO3 solution of 0.01M for 2-3 days. The ratio of member constituents, time of contact and concentration of equilibrating solution were properly adjusted to obtain the best potential response.
POTENTIOMETRIC RESPONSE:
All the potentiometric measurements were performed at constant temperature of 25 ± 0.5°C by digital pH meter (Elico L1-10 India). Saturated calomel electrode was used as a reference electrode. The potential across the membrane was measured by setting up the following cell assembly.
External 0.1M AgNO3 PVC Test Internal
SCE Membrane Solution SCE
The concentration of the test solution was varied in the range of 1.0 × 10-8 to 1.0 ×10-1 M.
TREATMENT OF THE ELECTROPLATING WASTE:18
The electroplating waste (40 ml) was first filtered and 5 ml conc. H2SO4 was added. The final solution was made upto 50 ml maintaining the pH between 3-4 and solution was suitably diluted.
RESULTS AND DISCUSSION:
5-MeOSalps was employed as Ag+ ion selective ionophore in the preparation of silver ion selective electrode. The potential responses of various ion selective electrodes are shown in Fig.1. The measurements were performed in the concentration range of 1.0 ×10-6 to 1.0 × 10-1 M AgNO3. The different electrodes show linear response in concentration range from 1.0 × 10-1 to1.0 × 10-5 M. The fig.1 reveals that only Ag+ ions shows nearly nernstian slope of 59 mV per decade. The results thus indicate that silver ions are more easily attracted to the PVC 5-MeOSalps membrane, resulting in a nernstian potential response over a wide range.
Fig.1 Potential response of various ion selective electrode based on the ligands 5-MeOSalps. 1: refers to Ag+ 2 : refers to Hg2+ 3: refers to Na+, K+, Rb+, Cs+ , Mg2+, Ca2+, Ba2+, Cu2+, Co2+, Ni2+, Zn2+, Pb2+, Cd2+.
The sensitivity and selectivity obtained for a given ionophore depends significantly on the membrane ingredients, nature of the solvent and the additive used19-22. Therefore the influence of membrane composition on the potential response of Ag+ was investigated. Plasticizers are frequently used to enhance the response characteristic e.g. working concentration range, slope etc. The effect of addition of the plasticizer to membrane was, therefore, studied and significantly improvement with ligands to working concentration range and slope has been observed. The effect of plasticizers (DBP, BA, and NPOE), additive (NaTPB and KTK) and amount of ion carriers on the performance of the membrane was studied. Among the solvent mediator used DBP shows the best sensitivity with membrane no.11 i.e. use of 33% PVC, 5% 5-MeOSalps, 60% DBP, 2% NaTBP result in the nernstian slope of 58.2 ± 0.3 mV per decade over a wide dynamic range. It may be noted that the presence of lipophilic negatively charged additives not only diminishes the ohmic resistance23 but also enhances the response. Moreover the additives may catalyze the exchange kinetics at the sample membrane interface. Table-1 shows that the presence of 2% NaTPB as additive increases the slope of sensor to 58.2 mV per decade.
The calibration parameter, response time and life time of different membrane have been determined. Electrode presented nernstian slope of 58.2 ± 0.3mV/decade (Fig. 2) for Ag+ ions over a wide concentration range of 1.0 ×10-1 to 8.0 ×10-6 M with detection limit, as determined from the intersection of the two extrapolated segment of the calibration graph 5.0 ×10-6 M (0.54 µgmL-1). The concentration of the internal solution (AgNO3) of the electrode was changed from (1 × 10-3 to1 × 10-5 M) and it is found that variation in the internal solution concentration does not cause any significant change in the potential response of Ag+.(Fig. 3). A 1.0 ×10-4 M AgNO3 solution gives smooth functioning of electrode system. The sensor has a short response time of 5 s. The potential remain constant for more than 5 min. and after that it shows slow divergence (Fig. 4).
TABLE -1 Optimization of Membrane Composition
|
COMPOSITION (%) |
||||||||
|
Membrane No. |
PVC |
5-Meosalps |
DBP |
BA |
NPOE |
KTK |
Na TPB |
SLOPE (mV/ Decade) |
|
1 |
33 |
1 |
66 |
---- |
---- |
---- |
---- |
0±0.3 |
|
2 |
33 |
2 |
66 |
---- |
---- |
---- |
---- |
5.6±0.1 |
|
3 |
33 |
4 |
65 |
---- |
---- |
---- |
---- |
11.3±0.2 |
|
4 |
33 |
5 |
63 |
---- |
---- |
---- |
---- |
15.9±0.1 |
|
5 |
33 |
6 |
62 |
---- |
---- |
---- |
---- |
23.5±0.3 |
|
6 |
33 |
5 |
61 |
---- |
---- |
---- |
---- |
23.2±0.1 |
|
7 |
33 |
5 |
---- |
61 |
---- |
---- |
---- |
21.5±0.2 |
|
8 |
33 |
5 |
---- |
---- |
60 |
---- |
---- |
20.9±0.3 |
|
9 |
33 |
5 |
60 |
---- |
---- |
2 |
---- |
49.9±0.1 |
|
10 |
33 |
5 |
59 |
---- |
---- |
3 |
---- |
47.3±0.2 |
|
11 |
33 |
5 |
60 |
---- |
---- |
---- |
2 |
58.2±0.3 |
|
12 |
33 |
5 |
---- |
60 |
---- |
---- |
2 |
51.7±0.1 |
|
13 |
33 |
5 |
---- |
---- |
60 |
---- |
2 |
51.5±0.2 |
|
14 |
33 |
----- |
65 |
---- |
---- |
---- |
2 |
09.5±0.3 |
Fig: 2 Calibration graph of silver ion selective electrode based on 5-MeOSalps with membrane no.11
Fig: 3. Effect of concentration of internal reference solution concentration on the electrode response; (A) 1.0 × 10-3 M (B) 1.0 × 10-4 M (C) 1.0 × 10-5 M
The pH dependence of electrode potential of 1.0 × 10-4 silver ion was tested over the pH range of 4.5 -10.5. The pH was maintained by introducing small drops of HNO3 (0.1M) or NaOH (0.1M) (Fig. 5). The potential difference was independent of the pH in the range of 4.5-10.5. At a pH greater than 9.5, the deviation is due to the formation of some hydroxyl complexes of silver ion.
Fig: 4 Static response time of silver sensor based on 5-MeOSalps using a 1.0 × 10-4 M solution of AgNO3.
Fig. 5. Effect of pH of the test solution (1.0 × 10-4 M of AgNO3) on the potential response of the silver sensor.
TABLE-2 Selectivity Coefficient of Various Inferring Ions (Mn+)
|
Cations |
K(MPM) |
|
Na+ |
1.2 x 10-4 |
|
K+ |
1.4 x 10-4 |
|
Rb+ |
2.2 x 10-4 |
|
Cs+ |
2.5 x 10-4 |
|
Cu2+ |
3.0 x 10-4 |
|
Co2+ |
4.5 x 10-4 |
|
Ni+2 |
2.5 x 10-4 |
|
Zn+2 |
3.2 x 10-4 |
|
Cd+2 |
1.7 x 10-4 |
|
Pb+2 |
1.8 x 10-4 |
|
Hg+2 |
2.1 x 10-4 |
|
Ca+2 |
6.1 x 10-4 |
|
Mg+2 |
3.3 x 10-4 |
|
Ba+2 |
7.3 x 10-4 |
TABLE-3: Comparison of Serious Interfering Ion of Different Silver Ion Selective
|
Ionophore |
Serious interfering Ion |
Slope mV/Decade |
Detection Limit |
Ref. |
|
Bis(3-PyridineCarboxylate ) |
Hg2+ |
57.0 |
1.0 10-5 |
27 |
|
Calix[4]arene Calixarene (containing nitrogen) |
Hg2+ |
47.0 |
8.0 10-6 |
28 |
|
Calixarene derivatives (allyl, benzyl, |
Tl+,Na+,Li+,Hg2+ |
57.0 |
5.0 10-5 |
29 |
Selectivity is perhaps the most important characteristic of any sensor which defines the nature of the device and the extent to which it may be employed in the determination of particular ions in the presence of other interfering ion. To investigate the selectivity of proposed membrane electrode its potential response was investigated in the presence of various interfering ions using matched potential method (MPM)24-25. According to this method the selectivity coefficient is defined as the activity (concentration) ratio of a primary ion and the interfering ion26 which give the same potential change in the reference solution. The resulting values obtained for proposed silver ion selective electrode was summarized in Table-2. It is seen that alkali, alkaline earth and transition metal ions used did not disturb the functioning of silver ion selective electrode. In Table-3 serious interfering ions, slopes and detection limits of different ion selective electrode based on different ionophore are compared with those of this work. It is seen that not only the detection limit of the proposed sensor, but also its slope and serious interfering ion are superior to those for other silver ion selective electrode27-29.
APPLICATION:
The proposed membrane electrode was found to work under laboratory condition. The sensor was used as an indicator electrode for the titration of silver ion with EDTA. The result (Fig.-6) indicates the amount of silver ion (1.0 × 10-4 M) can be determined with the electrode.
Fig. 6 Potentiometric titration curve of silver ion solution with EDTA, using a proposed sensor as an indicator electrode.
It was successfully applied for the direct determination of the silver in waste water sample from local electroplating factory. The silver content obtained from three replicate measurements was found to be in satisfactory agreement with that obtained by atomic absorption spectrometry.
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Received on 05.04.2010 Modified on 10.05.2010
Accepted on 22.05.2010 © AJRC All right reserved
Asian J. Research Chem. 3(3): July- Sept. 2010; Page 772-775