Chloride-induced corrosion of steel embedded in mortars containing fly ash and spent cracking catalyst
Introduction
Corrosion of reinforcing steel is of great concern because it is probably the most widespread cause of degradation in reinforced concrete. Initially, reinforcing steel embedded in concrete is naturally protected from corrosion by the high alkalinity of its pore solution [1]. However, this passive state can be broken by the destruction of the passive film that protects steel reinforcement. The main agents leading to destruction of the passive film are penetration of chlorides and carbon dioxide.
Zeolitic catalysts are widely used in petrochemical refining (400,000 tons/year). When the catalytic properties of this product are degraded, the deactivated catalyst must be replaced. Its chemical composition, based on silicoaluminates, together with its zeolitic structure, can be used in concrete, due to its high pozzolanic activity. However, it also increases slightly water demand of mixtures, which can lead to a loss of workability [2], [3], [4], [5], [6], [7], [8], [9], [10].
FC3R is the residue of this zeolitic catalytic cracking catalyst, so it is the product once it has lost its catalytic activity. Additionally, FC3R has a high amount of Al2O3, which can bind chlorides coming from external sources thereby reducing the potential for corrosion of reinforcements.
Fly ashes have been used in concretes, because of their pozzolanic activity and because they significantly improve workability by their round-shaped particles [11], [12], [13], [14], [15], [16], [17].
For these reasons, a combination of both pozzolans, can contribute to increase cement substitution in concrete, without a loss in workability, and improve mechanical properties and chloride ingress resistance.
The aim of this work is to evaluate the behaviour of portland cement-FC3R-fly ash mortars in a chloride-contaminated environment. Chloride migration tests were used to determine the chloride ingress resistance of mortars, and the corrosion rates of reinforcing steels embedded in these mortars were monitored when exposed to external chlorides and carbonation.
Section snippets
Materials and sample preparation
All mixtures were prepared using portland cement type CEM I 52.5 R, siliceous aggregate, FC3R (supplied by BP España), fly ashes and tap water. Table 1 compares chemical compositions of cement, fly ash and FC3R. In some mixtures Sika Viscocrete plasticizer was used. Mortars were prepared with a water/cementitious material ratio (w/cm) of 0.4 for specimens used in the migration tests and 0.5 in the corrosion tests. The sand/cementitious material ratio was 3. The migration test specimens were
Migration tests of portland cement-FC3R-fly ash mortars
Fig. 4 shows resistivity measurements of mortars at 28 days of curing time, before they were used in the migration tests. All mortars with pozzolanic substitution showed high resistivity values compared with the plain cement mortars (“Control” and “Plast”) because the pozzolanic reaction produces a denser pore structure due to the formation of additional hydration products in the pores of the mortar. These results suggest that pozzolanic mortars (“FC3R-Plast”, “FA”, “FC3R-FA” and
Conclusions
This research has shown that portland cement-FC3R-fly ash mortars do not add any additional risk under an external chloride attack. These mortars have higher chloride ingress resistance as it has been pointed out by the lower chloride diffusion coefficients obtained for mortars with FC3R and FA. Once corrosion is initiated, the corrosion rate level of steel is similar to that in a control mortar. When combined chloride/carbonation attack is foreseeable the use of these ternary mixed could be
Acknowledgements
This research was supported by Ministerio de Ciencia y Tecnología, Spain (Project MAT 2001-2694). E. Zornoza thanks to Ministerio de Ciencia y Tecnologia for his Doctorate Grant (FPU Programme, Ref. AP2002-3421).
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