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In order to examine the resistance to acidic solution of the different concrete compositions, an accelerated degradation test was carried out employing the apparatus developed by De Belie et al. (2002). The accelerated test procedure was based on the combination of a chemical action (wetting in an acid solution and drying in air) and a mechanical action (brushing).

Three toroid specimens were casted in a special mould for testing each concrete batch. The mould presented an internal diameter of 40 mm, an external diameter of 270 mm and a height of 70 mm.

In addition, the mould contained the anchoring mechanisms needed for the attachment of the specimen into one axle of the apparatus and for the metallic piece serving as the trigger for the beginning of the laser measurements.

The testing machine (Figure 3.42a) consisted of four horizontal rotating stainless steel axles, each one able to contain two sets of three samples turning through their own container and covered by a shared case to avoid evaporation. A switch gear manually actioned made possible the variation in the rotating speed between 1.04 and 24.41 revolutions per hour. The equipment also permitted the coupling of the brushing device (Figure 3.42b) and laser device (Figure 3.42c) to a fixed position on the frame of the apparatus by use of two stop pieces and two bolts. A more detailed description of the apparatus can be found in De Belie et al. (2002).

115 Figure 3.42: TAP apparatus

After 28 days of curing, the concrete specimens were installed into the accelerated degradation tests (TAP) apparatus with two clamping rings, and a stainless steel angle (10x10 mm) was screwed by means of two bolts into each sample. Each test container was filled with two litres of acid solution composed of 30 g/l of acetic acid and 30 g/l lactic acid, which affected only to the outer bottom part of each specimen.

One accelerated degradation cycle consisted of the immersion of the samples in a fresh acid solution during 7 days, followed by a 2 hours air-drying period before 3 brushing steps - in alternate direction of rotation - to remove the degraded concrete weakened by the chemical attack. Whilst the low rotating speed was selected during the acid immersion, the brushing step was performed with the samples rotating at high speed by means of three rotary brushes with 20 mm long white nylon hairs turning at 394 rpm. This testing sequence was repeated until 6 attack cycles were completed. Previous to the testing procedure and after each attack cycle, the distance between the samples and the laser sensors was determined by means of optical triangulation and registered as a means to evaluate the change in radius due to the degradation process. All the measurements - 4 contour parallel lines separated 0.50 mm per specimen - were performed in steps of 0.24 mm with the samples turning at high speed. In addition, the evolution of the degradation was evaluated visually and the pH of the solution was measured at the beginning and at the end of each attack cycle.

(a)

(b) (c)

116

The laser measurements were employed to calculate the degradation depth by comparing the radius change through the experiment. Moreover, the surface roughness (3.37) was calculated as the arithmetical average value of the departure y(x) (mm) of the profile above and below the centre line throughout a prescribed sample length, based on ISO 4287 (1997).

Ra= 1

SL∙ SL|y x |dx

0

(3.37)

with Ra the surface roughness [mm], SL the prescribed sampling length [mm] and y(x) the profile height function [mm]. Given that a 50 mm sampling length was chosen (De Belie et al., 2002), thirteen Ra values were obtained per contour profile.

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1. INTRODUCTION

The emergence of the use of recycled materials in the construction industry, specifically in the production of concrete, has met with varying degrees of success due to the barriers that the market for recycled products has still to overcome. Since to a large extent, the quality of the concrete mixture depends upon the properties of the raw materials used in its manufacture; the quality of the recycled aggregates is perceived as an obstacle in the recycling of construction and demolition wastes (CDW) as secondary aggregates for concrete. Nonetheless, numerous scientific studies show that it is possible to obtain good quality, economic and environmentally friendly building materials when the coarse fraction of CDW recycled aggregates is used appropriately.

This chapter presents an overview of the significant characteristics of the different constituents to be used in the conventional and recycled concrete mixtures. From a quality point of view, special attention was paid to the recycled coarse aggregates since their heterogeneous nature strongly affects their quality. Thus, a thorough physical, mechanical and microstructural characterization was carried out in order to assess the suitability of their use in the concrete manufacture in accordance with the requirements set for natural aggregates in the current Spanish legislation.

Nevertheless, note that the Spanish Code on Structural Concrete (EHE-08) (Permanent Commission on Concrete, 2008) does not take into account the use of mixed recycled aggregates in the concrete manufacture, not even in a non-structural capacity.

Chapter

Concrete raw

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