Chromate – analytics and long-term stability
All manufacturers of cement and cementitious preparations have had to comply with the specifications of the European Chromate Directive 2003/53/EC since January 17, 2005. Accordingly, cement or cementitious preparations must not contain more than 2 ppm water-soluble chromate relative to the mass of dry cement. The European standardisation committee CEN elaborated a harmonised European test method EN 196-10 to determine this content.
Does analysis according to EN 196-10 require an oxidation step?
The standard does not comprise an oxidation step to take into account reducing substances. These may reduce the chromate during the analysis process, which yields a lower content of water-soluble chromate. This effect is to be counteracted by precise adjustment of the analysis solution pH to a value between 2.1 and 2.5.
Comparison tests carried out on different European cements to determine chromate according to EN 196-10 showed that the differences between the results obtained with and without oxidation were smaller than those recorded in interlaboratory trials in which the process described in the Technical Rules on Hazardous Substances (TRGS 613) had been applied. The results either tallied within the range of test variation, or the analysis results recorded without oxidation were slightly lower than those obtained when an oxidation step was performed.
Investigations carried out by the Research Institute revealed that the lower values were not attributable to the omission of the oxidation step, but rather to slight temporal differences in the analysis. As a consequence of these differences, not all the pretreated cement extracts exhibited the typical red-violet coloration of the DPC-Cr(III) complex. In some cases, the test solution was red instead of red-violet (Fig. 1). This observation, which had been made by visual inspection, was confirmed by the UV/VIS spectra of the solutions. In the chromate solution, the DPC-Cr(III) complex absorbs visible light. The absorption maximum ranges around a wavelength of about 540 nm. In the processed cement extract, by contrast, a solution component absorbs with an absorption maximum at a wavelength below 350 nm additionally. This generates a slightly yellow coloration and the yellowish portions in the solution cause the analysis solution as a whole to become red instead of red-violet. Obviously, another cation reacts with the diphenyl carbazone to form a complex generating yellow coloration. As a consequence, the concentration of the DPC-Cr(III) complex in the solution is reduced, which results in a deficiency in the findings of hexavalent chromium. Competing reactions did not occur during chromate analyses in which diphenyl carbazide was added immediately after acidification or which had a pH value of less than 2. A reduction of the pH value below 2, however, requires a prior oxidation step. |
Chromate analysis in cementitious preparationsThe determination of the water-soluble chromate content in cementitious preparations is similar to that of cements. Preparations are first suspended in water and subsequently filtered. Cementitious preparations may still be too “dry” after water addition to allow extraction of a sufficient quantity of filtrate. In these cases, the quantity of water added has to be increased to the extent required for extracting a sufficient quantity of filtrate. Performing an oxidation step prior to lowering the pH value for chromate analysis is advantageous for the investigation of cementitious preparations. The aqueous extracts of tile adhesives, fillers and some other cementitious preparations display milky cloudiness. This cloudiness is attributable to organic additions, and its elimination requires considerable preparative efforts – provided that it is possible in the first place. Chromate analysis, however, presupposes an absolutely clear analysis sample as the cloudiness leads to unspecific absorption during spectrophotometric measurement, thus resulting in too high analysis results. If the extract is heated upon addition of a suitable oxidising agent first, the organic additions are modified in such a way as to be easily filtered or decanted. The cloudiness no longer causes any problems then.
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Durability of chromate reductionThe reduction of bagged cements has been primarily accomplished by adding ferrous sulphate compounds in the form of granulate so far. The crystal water contained in this granulate may react with the cement to form a capsule of cement hydration products. Although this capsule reduces the solubility of the compounds, it also conserves the core of the ferrous sulphate particles. This conservation enhances the durability of reducing efficacy. When the cement sample is suspended or when the cement is processed, the encapsuled particles are comminuted mechanically, which accelerates their dissolution. If, however, the chromate reducing agent in the cement is fine-grained, a hydrate layer is formed around the particles of the chromate reducing agent as well, but the mechanically aided dissolution of the reducing agent is possible to a limited extent only. Such a fine-grained structure of the reducing agent is obtained when it is ground together with the cement or the cement components. For that reason, the cement industry has increasingly used tin(II) sulphate free of crystal water when the chromate reducing agent is metered in this way. The costs incurred for the use of tin(II) compounds are, however, significantly higher than those for reducing agents based on ferrous sulphate. The Research Institute is therefore conducting trials on ferrous sulphates low in crystal water. The trials are to clarify whether these compounds can be of any help in reaching a compromise between technically convenient metering and adequately durable reducing efficacy. |
Literature
Puntke, St.; Wassing, W.: Technische Zusammenhänge bei der Herstellung und Analyse chromatarmer Zemente. Zement-Kalk-Gips 55 (2002), Nr. 3, S. 82-93 |
Schneider, M. ; Lipus, K.: Chromatarme Zemente für einen verbesserten Arbeitsschutz. Zement-Kalk-Gips 55 (2002), Nr. 6, S. 86-95 |
Baetzner, S.: Lösungswege für die Analyse von Eisen(II)-sulfat-Hydrat im Hinblick auf dessen chromatreduzierende Wirkung in Zement. Zement-Kalk-Gips 55 (2002), Nr. 7, S. 80-88 |



