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Euradwaste '08 - EU Bookshop - Europa

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3. Results<br />

3.1 Concrete<br />

(M) log P CO2 = -2.65<br />

Carbonatation is one of the most relevant processes in concrete degradation. Presence of calcite is<br />

greater in the hydration area (Fig. 2a); whereas the rest of precipitates are found in the pores close<br />

the interface with the bentonite. Portlandite begins to precipitate in this area until cover all the sample<br />

surface (Fig 2b, 2c).<br />

6 μm<br />

Figure 2. (a) Crystals of Ca CO3 on the sample surface (b) Ca (OH)2 covering concrete surface(c)<br />

detail of crystals<br />

As well, gypsum crystals were observed (Fig.3). They come from the reaction of substitution between<br />

portlandite and sulphate present in the hydration solution.<br />

40 μm 40 μm<br />

Figure 3. Gypsum crystals in a micro fracture.<br />

(a) (b) (c)<br />

3.2 Interface concrete/bentonite<br />

A homogeneous white precipitate is formed at the interface. The thickness of this layer is around 2<br />

μm. The SEM-EDX analysis of a cross-section of this area shows the formation of a continuous<br />

layer of portlandite. Other secondary mineral phases were found at the interface: calcium silicate<br />

hydrates or CSH gels tobermorite-type with Ca/Si molar ratio of 0.6, magnesium hydroxide (brucite)<br />

and ettringite (Aft) (Ca6Al2(SO4)3(OH)12 26(H2O)) (Fig. 4). Also, dissolution of quartz was<br />

detected .This process enables the precipitation of CSH minerals such as tobermorite.<br />

Tobermorite<br />

6�m 6�m<br />

455

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