Electrochemical reduction of corrosion products found on lead artefacts Redha Amri, Hénia Mousser* Département de Chimie Industrielle, Faculté des Sciences de l’Ingénieur, Université Mentouri Constantine, 25000 Constantine, Algérie. bouzidi_henia@yahoo.fr Mohamed Fakhri Bencharif Laboratoire des Mesures Electrochimiques, Département de Physique, Faculté des Sciences Exactes, Université Mentouri Constantine, 25000 Constantine, Algérie André Darchen UMR CNRS n°6226 Sciences Chimiques de Rennes, ENSCR, Avenue du Général Leclerc, CS 50837, 35708 Rennes cedex 7, France Abdelhamid Mousser Département de Chimie, Faculté des Sciences Exactes, Université Mentouri Constantine, 25000 Constantine, Algérie Abstract—Electrochemical restoration of corroded lead artefacts should be able to consolidate the objects and reverses the corrosion products in to initial metallic state. Cerussite (PbCO 3), anglesite (PbSO4), cotunnite (PbCl2) and lead oxides are the most responded corrosion products found on the lead artefacts. The knowledge of the reduction potential of the lead corrosion products is primordial for an appropriate action in the restoration process. The electrochemical reduction of the cerussite and the anglesite into metallic lead on platinum substrate, in the sodium sulphate and the sodium carbonate solutions (0.5M) was investigated. This work is a part of a project aiming to perform the restoration of numerous archaeological coins. The reduction’s potentials are determined by linear sweep voltammetry and corroborate by potentiostatic conditions. The transformation of lead corrosion products into metallic lead was carried out both in the sulphate and the carbonate medium. Keywords: Electroreduction; cerussite; anglesite; lead; reduction. Introduction Many ancient lead artefacts are nowadays conserved in museums, many of them are badly corroded that it becomes extremely fragile and all surface are just a mass of corrosion products. Depending on the characteristic of the archaeological site in which the lead artefacts are found and the environment where they are exposed or stored, the lead objects are transformed to Anglesite (PbSO4), hydroxycarbonate compounds such as cerussite (PbCO3), hydrocerussite Pb(CO3)2(OH)2), cotunnite (PbCl2) and lead oxides (PbO, PbO2). These corrosion’s products were currently found on several archaeological objects dating from the Iron Age [1-8]. Many analytical methods have been used to identify the chemical composition of archaeological artefacts [3, 5-9]. Electrochemical treatments of severely corroded objects have to transform the corrosion’s products into the metal mass. Some studies were carried out to determine the potential reduction of lead corrosion products [3, 10-12]. According to the Pourbaix diagram [13], the lead is stable in the neutral or the alkaline solutions which are free from oxidizing agents. In the soil, the carbonate ions are usually present so basic lead carbonates and lead oxides were formed with most archaeological objects when these last are made of lead. The gray lead carbonate and lead oxide often form a protective layer on the artefact that it prevents further oxidation [1]. Both these corrosion’s compounds are found on lead from a marine environment, lead chloride, lead sulphide and lead sulphate [1]. This work is the second part of a project aiming to perform the restoration of numerous archaeological Numidian coins [5]. The research is carried out to provide more data on the electrochemical restoration process of lead archaeological objects and to determine the conditions of electrochemical reduction of some lead corrosion’s products found on the Numidian archaeological artefacts [5]. I. EXPERIMENTAL All the solutions were prepared using distilled water and reagent grade chemicals. The cerussite and the anglesite were prepared according to the literature [14-16]. All products were identified by X-ray diffraction and InfraRed beam. The electrochemical experiments were carried out in a threeelectrode thermostated cell with a PAR 373A potentiostat coupled with a Kipp and Zonen XY recorder. A rectangular platinum plate (2.5 cm2) and a saturated calomel electrode (SCE) were used as working and reference electrodes, respectively. Before each experience, the Pt working electrode was mechanically polished with successively finer grades of SiC emery papers and was rinsed with distilled water. In order to eliminate residual oxides formed on the working electrode a fixed reduction current density was applied (0.05mA/cm2) for 10 min [17]. In each electrochemical measurement a paste of lead compound was prepared. A mixture of the corresponding compound and distillate water was spread over the surface of the working electrode, so that the entire electrode surface was covered completely. The reduction potential of each compound was investigated by linear sweep voltammetry between the potential at open circuit and -1.4V with 1 mV/s scan rate. The potentiostatic data were carried out for each determined potential value. All experiments were realized at room temperature. XRD was performed with an X’Pert PRO MRD diffractometer (CRD, SONATRACH of Boumerdes, Algeria) equipped with a PANalytical's XRD Data Collector systems and a Panalytical HighScore Plus software. The spectrometer is provided with a copper anticathode (λ= 1.5401A˚, I = 30mA and V = 40 kV). Sweeping was made between 2 and 70◦ (2θ) with a count-time of 46 s for each step of 0.017◦ (2θ). II. RESULTS AND DISCUSSION II.1. DRX analysis Cerussite and anglesite prepared [14-16] were identified by Xray diffraction. The XRD difractogramms of these products are presented in Fig. 1 and Fig. 2. In Fig. 1, the most intense peaks are observed at: dhkl = 3.59; 3.49; 2.48 and 2.08 Å. According to the ASTM file No 47-1734 [18], these peaks indicate that the formed product is the cerussite. Fig. 2: XRD spectrum of the anglesite. II.2. Reduction of the cerussite The figure 3 shows voltammetric curve of cerussite on platinum substrate in sulfate and carbonate electrolyte solutions. In the sodium sulfate electrolyte (solid line) a small cathodic peak can be seen (approximately at -0.68V versus SCE) with a small current (153µA). This peak indicates the beginning of cerussite reduction. Beyond this peak the current fall a little and take a constant value (~ 80µA) in this region the cathodic process is controlled by diffusion [17]. Immediately after this region the current rise again, due to the hydrogen evolution reaction occurring in parallel with cathodic reaction of cerussite. In sodium carbonate electrolyte (dash line) a cathodic reaction occurs at more negative potential. The peak is observed approximately at -1.18V versusSCE,with 3.85mA and indicates occurring of the reduction of the cerussite. After this point the current fall and increase at more negative potential due to the hydrogen evolution. The reduction of the cerussite was affected kinetically by the nature of the bath, since de peak current value is more important in the carbonate bath than in the sulfate one. Moreover the nature of the bath affects the reduction of cerussite thermodynamically and the potential of the peak in the carbonate bath shifts to more negative values. Fig. 1: XRD spectrum of the cerussite. Fig. 2 shows the XRD diagramm of the anglesite phase which is identified by the peaks observed at: dhkl = 3.01; 3.34; 3.22 and 4.27Å from ASTM file No 36-1461 [18] (dhkl = 3.007; 3.33; 3.21 and 4.265Å). Fig. 3: Voltammetry of cerussite. (a) In Na2SO4 (0.5M). (b) In Na2CO3 (0.5M). To corroborate these potentials the cerussite was treated at 1.18V in carbonate solution (0.5M), (Fig. 4, a) and at -0.68V and at -1.08V in sulfate solution (0.5M), (Fig. 4, b). The figure 4 shows that, in carbonate medium, a high current is measured in the first hour of treatment. The electrochemical reduction of the cerussite occurred at -1.18V (Fig. 4, b). At the end of the treatment, the current density tends to zero and the white cerussite was transformed to a grey metallic lead. In the sulfate solution, the end of the cathodic reaction was observed, with a low rate, at -0.68V. At -1.08V, the electrochemical reduction of the cerussite is fast and the measured current is more important than that measured at -0.68V. The potentiostatic treatments of anglesite in the carbonate bath at -0.73V and -0.87V were carried out and the results are presented in the figure 6. At -0.73V no current is measured and no change occurs in the nature or the appearance of the anglesite. At -0.87V, a high current is observed and at the end of the treatment (Fig. 6, (a)), the anglesite is transformed into metallic lead. The anglesite shows the same behavior in sulfate solution (0.5M) at -0.93V (Fig. 6, (b)). Fig. 6: Electrochemical reduction of anglesite. (a) In Na2SO4 (0.5M). (b) In Na2CO3 (0.5M). Fig. 4: Electrochemical reduction of cerussite. (a) In Na2SO4 (0.5M). (b) In Na2CO3 (0.5M). II.3. Reduction of the anglesite The figure 5 presents the voltammetric curve of anglesite. Two cathodic peaks appear in sulfate solution. The anglesite reduction (Fig. 5, (a)) occurs at -0.73V versus SCE. The second reduction is observed at -0.93V versus SCE and is probably due to the bulk reduction. In the carbonate electrolyte, the electroreduction’s peak appears at 0.83Vversus SCE (Fig. 5, (b)). The reduction of anglesite is affected by the nature of the bath. The potential reduction of the anglesite shifts to more negative potential values in the carbonate medium. Conclusion The electrochemical studies of the two corrosion products cerussite and anglesite which were formed on the lead surface, in the sulfate and the carbonate electrolytic baths, revealed the reduction of cerussite and anglesite into metallic lead. In the sodium carbonate solution (0.5M), the potential -1.18V can reduce all corrosion products and the potential -1.1V is sufficient for the same reduction in the sodium sulfate bath (0.5M). The results show that the nature of the electrolytic bath controls the electrochemical process of the reduction thermodynamically and kinetically. The electrochemical reduction of the cerussite and the anglesite, in Na2SO4 or in Na2CO3 is characterized by a first peak (thin lead film) and by a second one (bulk reduction), where the rate of the reduction was high in the region of the second peak and controlled by diffusion. However in Na2CO3, the reduction takes place at more negative potentials with a single cathodic peak. ACKNOWLEDGMENT The authors express their appreciation to Mentouri University of Constantine for its financial support necessary to carry out this study, and their thanks to sirs Mustapha Belkadi and Khaddja Gellil, Engineers at the Laboratory CRD, SONATRACH of Boumerdes, Algeria for XRD measurments. REFERENCES [1] [2] Fig. 5: Voltammetry of anglesite. (a) In Na2SO4 (0.5M). (b) In Na2CO3 (0.5M). [3] D. L. Hamilton, “Methods of Conserving Archaeological Material from Underwater Sites”, Department of Anthropology Texas A & M University College Station, 1999. R. Gettens, “The Corrosion Products of Metal Antiquities”, Smith Sonian Institute Publication, Washington, 1964. E.Rocca, F Mirambet, J Steinmtz, Journal of Mineral Science, 39, 2004, pp. 2767–2774. [4] A. Niklasson, L. G. Johansson, J. E. Svensson, Proceedings of Metal, 2004, pp. 273–280. [5] H. Mousser, R. Amri, A. Madani, A. Darchen and A. Mousser, Applied Surface Science, 257, 2011, pp. 5961–5965. [6] North, N. A., and I. D. 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