Thermal Studies and Analytical Applications of a Newly Synthesized Composite Material “Polyaniline Stannic Molybdate” ()
1. Introduction
Ion exchangers are always of large scale interest because of their higher selectivity and resistance at higher temperature. These materials have found large scale applications in water treatment and pollution control. An ion exchanger may be organic, inorganic or hybrid depending upon the nature of matrix of which it is made up of. Out of these, hybrid ion exchangers have received more attention because both organic as well as inorganic ion exchangers have some limitations. Organic ion exchangers are very sensitive to exposure to high radiation doses, which cause significant changes in their capacity and selectivity, presumably through hydrolysis of their functional groups, chain scission, and changes in their crosslinking. The inorganic ion exchangers have several superior qualities required for the treatment of industrial waste effluents compared to organic resins. In order to obtain a combination of these advantages associated with polymeric and inorganic materials as ion-exchangers, attempts have been made to develop polymeric-inorganic composite ion-exchangersby incorporation of inorganic monomers in the organic matrix. A composite ion-exchanger must be an interesting material, as it should possess the mechanical stability due to the presence of organic polymeric species and the basic characteristics of an inorganic ion-exchanger regarding its selectivity for some particular metal ions [1]. It was therefore considered to synthesize such hybrid ion-exchangers with a good ion-exchange capacity, high stability, reproducibility and selectivity for metal ions [2,3], indicating its useful environmental applications.
The work deals with the synthesis, ion exchange properties and thermal stability of polyaniline stannic molybdate, prepared by the incorporation of conducting polymer, i.e. polyanniline into the matrices of inorganic ion exchanger stannic molybdate.
2. Experimental
2.1. Reagents and Instruments
The main reagents used for the synthesis were aniline, stannic chloride pentahydrate and potassium persulphate (LobaChemePvt Ltd (India). All other chemicals and reagents used were of analytical grade. The main instruments used during the study were UV-vis spectrophotometer (Elico EI 301E, India), a PW 1148/89 based X-ray diffractometer (Phillips, Holland), a water bath incubator shaker (MSW-275, India) and muffle furnace (G1-111, India).
2.2. Preparation of Reagent
The solutions of 0.1 M Stannic chloride pentahydrate were prepared in demineralized water (DMW) and solutions of 10% (v/v) of double distilled aniline and 0.1 M potassium persulphate were prepared in 1.0 M HCl.
2.3. Preparation of Polyaniline Stannic Silicate
Polyaniline gels were prepared by mixing different volume ratio of 10% aniline and 0.1 M potassium persulphate with continuous stirring by a magnetic stirrer (Table 1). Green colored polyaniline gels were obtained by keeping the solution below 10˚C for half an hour [4]. A precipitate of stannic (IV) molybdate was prepared at room temperature (25˚C ± 2˚C) by adding mixture of 0.1 M sodium molybdate solution gradually to an aqueous solution of 0.1 M stannic chloride pentahydrate in different volume ratios. The white precipitates were obtained. The desired pH of the mixture was adjusted by adding HCl with continuous stirring. The gels of polyaniline were then added to the white inorganic precipitate of stannic(IV) molybdate and mixed thoroughly with constant stirring [5-7]. The resultant green color gels so obtained were kept for 24 h at room temperature (25˚C ± 2˚C) for digestion. The supernatant liquid was filtered off by suction. The gel was washed with demineralized water (DMW) till the filtrate was neutral. The product was dried in an oven at 50˚C. The dried material was broken into small granules on immersion in DMW. The granules were converted into H+ form by placing in 1 M HNO3 solution for 24 h. The excess acid from the material was removed after several washings with DMW and finally dried at 50˚C ± 2˚C. In this way a number of samples of polyaniline stannic molybdate were prepared in different experimental conditions described in Table 1. It was decided to study sample S-9 in detail on the basis of highest ion exchange capacity for Na+ ions.
2.4. Column Ion-Exchange Capacity
To determine the ion-exchange capacity, column process was used. 1.0 g dry cation-exchanger in H+ form was packed in a column (1.0 cm id) fitted with glass wool at the bottom. Metal nitrates as eluents were used to elute the H+ ions completely from the cation-exchanger column. The effluent was titrated against a standard solution of 0.1 M NaOH.
2.5. Thermal Stability
In order to determine the effect of heating temperature on ion-exchange capacity, 1.0 g sample of the material (S-9) in H+ form was heated at different temperatures in a muffle furnace for 1h and Na+ ion-exchange capacity was determined by standard column process as mentioned above.
2.6. Distribution Studies
The distribution coefficients (Kd) for various metal ions were determined in different concentrations of surfactant
Table 1. Synthesis of polyaniline stannic molybdate in different conditions.
A: 0.1M Stannic chloride pentahydrate; B: 0.1M sodium molybdate; C: 10% Aniline in 1.0M HCl; D: 0.1M K2S2O8 in 1.0M HCl.
(SDS).The effect of temperature on the distribution coefficient was also studied. Polyaniline stannic molybdate (0.3 g) in H+ form was put into 100 ml conical flasks each containing 30 mL solution of 0.1 M concentration of metal ions. The mixture was continuously shaken for a definite period of time at 30˚C, 45˚C, 60˚C and 75˚C (Table 2). The amount of metal ions present in the solution was determined by titrating it against disodium salt of EDTA (0.01 M) using standard procedures.
3. Results and Discussion
In this study of preparation and characterization of organic-inorganic composite cation exchange material, a number of samples of organic-inorganic electrically conducting composite stannicmolybdate providing a new class of hybrid ion-exchangers were prepared by sol-gel mixing of organic conducting polymer , polyaniline with the inorganic precipitate of stannic molybdate (Table 1). Among them, sample S-9 possessed enhanced Na+ ion exchange capacity (1.8 meq/g) and better thermal stability. Polyaniline gel was prepared by oxidation coupling using K2S2O8 in acidic aqueous medium.
The effect of temperature on the reaction seems to be very pronounced. Aniline underwent oxidation coupling only below 10˚C very effectively, leading to formation of polyaniline with fairly good yield.
However sample S9 of polyaniline stannic molybdate exhibited better granulometric and mechanical properties and reproducible behavior as is evident from Table 1. The samples prepared in various batches did not show any appreciable deviation in their ion exchange capacities. The ion exchange capacity of the composite cation exchanger for alkali metal ions and alkaline earth metal ions increases according to the increase in the hydrated ionic radius increases (Table 3). It was observed that on heating the material at different temperatures, ion exchange capacity of the dried sample material (S9) was changed as the temperature increased as shown in Table 4. From the comparative study of Na+ ion exchange capacity of polyaniline stannic molybdate with those of other ion exchangers, as shown in Table 5, it is apparent that this composite cation exchanger has more ion exchange capacity than others.
Table 2. Effect of temperature on theKd( mL·g-1 ) of metal ions in 0.1 M SDS.
Table 3. Ion exchange capacity of polyaniline stannic molybdate (sample S-9) for different metal ions.
Table 4. Effect of temperature on the ion-exchange capacity of polyaniline stannic molybdate.
Table 5. Comparison of ion exchange capacity of polyaniline stannic molybdate with those of other cation exchangers.
In order to explore the potentiality of polyaniline stannic molybdate in separation of metal ions, distribution studies of some metal ions were achieved in various concentrations of SDS. It is apparent from the data in Tables 2 and 6 that the Kd values varied with temperature and conc. of contacting solvents. The Kd values of metal ions increases up to 45˚C and then decreases, Thus 45˚C is the optimum temperature for the Kd value determination. It was also observed from kd values that the Hg(II) was highly adsorbed in all solvents while remaining metal ions were poorly adsorbed. The high uptake of Hg(II) in all solvents demonstrate not only the ion exchange properties but all the adsorption and ion selective characterization of the material. The utility of this compound has been demonstrated by achieving some binary separations (Mg2+-Hg2+, Cd2+-Hg2+ and Mn2+-Hg2+) of metal ions on its column. The separations were found to be quantitative and the results obtainedwere quite precise and accurate as is evident from Table 7. Hg2+ has also been selectively separated from a synthetic mixture of metal ions. The salient features of selective separation are summarized in Table 8. Thus we can say that this composite material is highly selective for Hg(II) and can be used for the separation of mercury from waste effluxents.
4. Conclusion
PolyanilineSn(IV) molybdate, an organic-inorganic com
Table 6. The distribution coefficients of metal ions in SDS (KdmLg−1) at 30˚C ± 2˚C.
Table 7. Quantitative Separations of metal ions in binary mixtures on a column of polyaniline stannic molybdate.
Table 8. Selective separation of Hg2+ from a synthetic mixture oh Hg2+, Cd2+, Mn2+ and Mg2+ on a column of polyaniline stannic molybdate.
posite cation exchange material represents a new class of ion exchange materials that combines good characteristics of both organic and inorganic components within a single composite. It is quite clear from the results that the composite cation exchanger has enhanced ion exchange capacity and thermal stabilities. The selective behavior of polyanilineSn(II) molybdate is important from environmental pollution chemistry point of view, where an effective separation method is needed for the removal of Hg(II) ions.
5. Acknowledgements
The authors are highly thankful to the H.O.D. Chemistry (Dr. S. A. Shah) and Director, National Institute of Technology (NIT) Hazratbal, Srinagar for providing the research facilities.
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