Journal of Analytical Chemistry., Vol.55, No. 11, 2000, pp. 1055-105Z Translatedfrom ZharnalAnaliticheskoi Khimii, Vol.55, No. 11, 2000, pp. 1176-1178. Original Russian TextCopyright9 2000 by Alekseev, Gorelog Kornilov. ARTICLES Membrane Electrodes Selective for Hydrogen Phosphate Ions 1 V. G. Alekseev, I. P. Gorelov, and M. V. Kornilov Tver State University, Sadovyi per. 35, Tver, 170002 Russia ReceivedDecember17, 1999;in finalform,March 22, 2000 Abstract--The possibility of using plasticized polyvinyl chloride film membranes with dispersed electroactive substances (MgNH4PO4, BiPO4, and CrPO4) for developing electrodes selective for hydrogen phosphate ions has been investigated. It is shown that a chromium(III) phosphate-based electrode is characterized by the linearity range 10-L10-6 M of the hydrogen phosphate function with a slope of 26.5 mV/pc and a satisfactory selectivity in the presence of chloride, nitrate, sulfate, and hydrogen carbonate ions. The determination of phosphoric acid salts is among the first problems that arise in the analysis of natural and waste waters. The spectrophotometric and gravimetric methods commonly used for determining phosphates are labor intensive and require laboratory conditions [1, 2]. In natural and waste waters, that is, in media close to neutral, soluble phosphates commonly occur as the hydrogen phosphate ion. Therefore, the development of a simple and highly sensitive electrode selective for hydrogen phosphate and suitable for direct potentiometric analysis under both laboratory and field conditions is needed. only the electroactive substance (EAS) but also the matrix material can affect the electrode properties [9]. Therefore, we decided to return to experiments with solid heterogeneous membranes using an alternative matrix material. The goal of this work was to study the possibility of developing an electrode selective for hydrogen phosphate ions based on a slightly soluble phosphate dispersed in a polyvinyl chloride matrix plasticized by dioctyl phthalate. As the electroactive substance, we used MgNH4PO4 (electrode I), BiPO4 (electrode II), and CrPO4 (electrode III). Only a few studies on phosphate-selective electrodes have been reported so far in the scientific literature. The following electrodes were suggested: an electrode with a liquid membrane based on organotin com- EXPERIMENTAL pounds (response to the HPO 2- and H2PO 4 ions) [3], electrodes with solid membranes based on an Ag2SP2S3 alloy (response to the H2PO4 ion) [4] and a mixture of silver and bismuth(Ill) oxide reduced by hydrazine in a Teflon matrix (response to the PO 3- ion) [5], a metallic cobalt electrode (response to the H2PO 4 ion) [6], and an enzyme electrode with response to the PO4aion [7]. These electrodes exhibit satisfactory analytical characteristics; however, they have not gained wide use so far for various reasons. Experiments were also performed with electrodes based on slightly soluble phosphates dispersed in a paraffin or synthetic rubber matrix, which are simpler to manufacture. A review of these publications is given in the monograph [8]. The author noted that all the electrodes studied were of low selectivity. At the same time, there is evidence that not Ipresented at the V All-RussianConferencewith the Participation of CIS Countries on Electrochemical Methods of Analysis (EMA-99), Moscow,December6-8, 1999. Preparation of electroactive substances. Magnesium ammonium phosphate. A required amount of 1 M KEHPO4 was added to a solution containing 1 M MgCI 2, 1 M NH4C1, and 1 M NH 3. A white curdy MgNHaPO4 precipitate formed. Bismuth(Ill) phosphate. A weighed portion of bismuth was dissolved in cone. HNO 3, and 1 M KEHPO4 was added. A white BiPO4 precipitate formed. Chromium(llI) phosphate. A 1 M Cr(NO3) 3 solution was added to 1 M KzHPO4. A violet CrPO4 precipitate formed. The precipitates obtained were washed by decantation, separated by centrifugation, and dried at a temperature of 80~ After these operations, CrPO4 passed from the violet form to a green one. Preparation of membranes. A weighed portion of polyvinyl chloride (PVC) was dissolved on heating in cyclohexanone, and a suspension of an electroactive substance in dioctyl phthalate was added. The solution was stirred until complete homogenization, poured into a Petri dish, and dried in air until complete evaporation of cyclohexanone. An elastic plasticized PVC film about 0.5 mm thick with the electroactive substance 1061-9348/00/5511-1055525.00 9 2000 MAIK"Nauka/Interperiodica" ALEKSEEV et al. 1056 Table 1. Electrochemical and analytical ~roperties of electrodes Electrode EAS EAS pK, [10] Electrode function slope, mV/pc Electrode function linearity range, M Detection limit, M Response time, s I MgNH4PO4 12.6 10.7 1001-1005 4x100 5 90 II BiPO4 22.9 85.0 1001_10-5 6 x 10--6 60 III CrPO 4 22.6 26.5 100L10-6 5x 10~ 60 dispersed in it was obtained. The membrane composition was as follows: PVC, 52.5%; dioctyl phthalate, 45.0%; electroactive substance, 2.5%. Preparation of electrodes. A disc 1 cm in diameter was cut from the finished membrane. This disc was pasted to an end of a PVC tube 1 cm in diameter and 10 cm in length with a solution of PVC in cyclohexanone. At the other end, the tube was closed with a tightly fitted polyethylene stopper with a silver wire covered with silver chloride that was passed through the stopper. The electrode was flooded with a solution containing 0.1 M KCI and 0.1 M K2HPO4 . Before performing measurements, the electrode was soaked in 0.1 M K2HPO4 for no less than 3 h. All the potentiometric measurements were performed at 20~ in reference to a saturated calomel electrode using an 1-135 potentiometer with an ion-selective electrode. To study the electrode function, a stock 0.5 M K2HPO4 solution was prepared from an accurately weighed portion; solutions with concentrations from 10-1 to 10-7 M were prepared by successively diluting the stock solution. The selectivity of electrodes was estimated by the separate solution method [9]. RESULTS AND DISCUSSION The potential of each electrode was constant over the pH range 6-10, which almost corresponds to the region of existence of the HPO 2- ion. The electrode function (Table 1) is linear over the range 10-1-10-5 M for electrodes I and II and over the range 10-1-10 -6 M for electrode III. It is evident that all the electrodes are characterized by low detection limits and short response times. Thus, the linearity range for electrode III is from one to three orders of magnitude wider and the detection limit is an order of magnitude lower than for the electrodes described in the literature [3-8]. This provides a reliable determination of HPO42- at a level of the maximum permissible concentration, which is equal to 3.5 x 10 -5 M [11]. The slope of the electrode function was close to the theoretical one only for electrode III. The selectivity coefficients of the electrodes relative to the inorganic ions most commonly occurring in natural and waste waters (CI-, NO~, HCO 3, and SO42-) are presented in Table 2. Electrode I is characterized by very low selectivity and is hardly suitable for the analysis of real multicomponent samples. The selectivity coefficients of electrodes II and III are acceptable, though they are worse by approximately an order of magnitude than those of the electrodes described in the literature. It is likely that the selectivity of the electrodes proposed can be improved by varying the ratio of membrane components. Thus, electrode III (based on CrPO 4) showed the best electrochemical and analytical properties; therefore, this electrode may be recommended for practical use. REFERENCES Table 2. Potentiometric selectivity coefficients relative to foreign anions (An) t eo, A. Electrode CI- so42- NO~ HCO~ I 1.29 1.98 4.67 3.31 H 0.50 0.40 0.49 0.32 III 0.52 0.41 0.70 0.39 1. Unifitsirovannye metody analiza rod (Standardized Methods of Water Analysis), Lur'e, Yu.Yu., Ed., Moscow: Khimiya, 1971. 2. Babko, A.K. and Pilipenko, A.T., Fotometricheskii analiz: metody opredeleniya nemetallov (Photometric Analysis: Determination of Nonmetals), Moscow: Khimiya, 1974. 3. Zarinskii, V.A., Shpigun, L.K., Shkinev, V.M., Spivakov, B.Ya., Trepalina, V.M., and Zolotov, Yu.A., Zh. Anal. Khim., 1980, vol. 35, no. 11, p. 2137. 4. Kish, P.P., Petrukhin, O.M., Balog, I.S., Gurzan, M.Ts., and Potapchuk, A.M., USSR Inventor's Certificate no. 1 649409, Byull. Izobret., 1991, no 18. p. 176. JOURNAL OF ANALYTICALCHEMISTRY Vol. 55 No. 11 2000 MEMBRANE ELECTRODES SELECTIVE FOR HYDROGEN PHOSPHATE IONS 5. Moskvin, L.N. and Ushenko, V.G., USSR Inventor's Certificate no. 1 580233, Byull. Izobret., 1990. no 27. p. 174. 6. Xiao, D., Yuan, H.-Y., Li, J., and Yu, R.-Q., Anal Chem, 1995, vol. 65, no. 2, p. 288. 7. D'Urso, E.M. and Coulet, P.R., Anal. Chim. Acta, 1990, vol. 239, no. 1, p. 1. 8. Lakshminarayanaiakh, N., Membrane Electrodes, New York: Academic, 1976. Translated under the title Membrannye elektrody, Leningrad: Khimiya, 1979. JOURNAL OF ANALYTICALCHEMISTRY Vol. 55 1057 9. Koryta, J. and Stulic, K., lontove-Selektivni Elektrody (Ion-Selective Electrodes), Prague: Academia, 1984. Translated under the title Ionoselektivnye elektrody, Moscow: Mir, 1989. 10. Lur'e, Yu.Yu., Spravochnik po analiticheskoi khimii (Handbook of Analytical Chemistry), Moscow: Khimiya, 1979. 11. Bespamyatnov, G.P. and Krotov, Yu.A., Predel'no dopustimye kontsentratsii khimicheskikh veshchestv v okruzhayushchei srede. Spravochnik (Maximum Permissible Concentrations of Chemical Substances in the Environment. Handbook), Leningrad: Khimiya, 1985. No. 11 2000
© Copyright 2026 Paperzz