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esults obtained so far. Most of the bibliographic references included refer to studies carried out<br />

during the project.<br />

2. Transport in crystalline rocks: PA relevant processes<br />

Groundwater chemistry<br />

RNs mainly migrate dissolved in the groundwater: the chemistry of the water (salinity, pH, Eh,<br />

complexing agents) is one of the main parameters controlling the aqueous speciation of RNs, their<br />

solubility and their retention in the medium. Chemistry influences several other processes, colloid<br />

formation and stability amongst others. When studying a crystalline medium, first key points are to<br />

understand what chemical reactions and sorption processes occur in the host rock (also in the presence<br />

of the engineered barrier) and what their effects on radionuclide mobility are (WP 4.1). Geochemical<br />

characterization includes the identification of water types and presence of elements affecting<br />

the water chemistry and its evolution (water/rock interactions, water paths, residence times,<br />

flow/mixing region, redox condition, effects of micro-organisms or colloids). Furthermore, to know<br />

if present geochemical models are able to account for these processes and if they are adequately<br />

calibrated in front of real systems is necessary.<br />

Site specific studies, as those carried out in the Swedish sites Forsmark and Simpevarp (WP4.5),<br />

represent a direct support for PA [6]. The evaluation of field geochemical data (Eh, pH, TOC, colloids<br />

presence, Mg-Ca, etc…) is needed to verify if they met safety criteria for site selection. On the<br />

other hand, these studies are fundamental to understand phenomena that cannot be obtained from<br />

laboratory studies. The understanding of the hydro-geochemical conditions of the past and present<br />

is the basis to predict future evolutions. Therefore, the complete characterization of a site allows<br />

gaining capability and confidence for the extrapolation of data when the information is scarce or not<br />

available. In certain environments as the Fennoscandian shield, the climate may have also very important<br />

effects. For this reason, different methodologies were implemented to understand the effects<br />

of glacial melt water intrusion [7].<br />

In-situ studies carried out at the FEBEX site serve to quantify mass transfer processes from the bentonite<br />

to granite, to perform in-depth analysis of the effects of the bentonite on the water chemistry<br />

and to analyse the presence and stability of bentonite colloids in realistic conditions. Attention is<br />

focused on hydro-geological structure (fractures, fault regions, lamprophyre...) previously identified<br />

[8]. Within FUNMIG, at the end of 2005, two investigation boreholes FU05.001 and FU05.002<br />

were drilled quasi parallel to the FEBEX gallery, and relatively near to the bentonite surface (30<br />

and 60 cm respectively) [9]. To characterize the crystalline rock, three short boreholes were additionally<br />

drilled for the geophysical experiments (FU05.003, -4 and -5) [8]. Several other boreholes<br />

around the gallery already existed (19 radial boreholes, FBX, Bous, etc.) that represent additional<br />

source of information both for hydro-geochemistry and hydrogeology. A schematic of FEBEX tunnel<br />

with the location of the new boreholes and main hydro-geological structures is presented in Figure<br />

1.<br />

Several water sampling campaigns were carried out for both water chemistry and colloid analyses.<br />

The waters from the new boreholes are slightly alkaline and with low electrical conductivity being<br />

very favourable conditions for bentonite colloid stability [4], so that this place is very adequate to<br />

study colloid generation and mobility processes. On the other hand, the migration through granite of<br />

conservative ions like I - and ReO4 - (installed in 1996 with the FEBEX experiment, Figure 1) and<br />

other “natural” tracers from the bentonite (Cl - , Na + ..) is being studied. I - was observed both in<br />

FU05.001 (interval 4, 0.46 ppm) and in FU05.002 (interval 3, 0.85 ppm) in correspondence to the<br />

initial location of the I - impregnated filter papers (Figure 1). The fact that only iodine and not rhenium<br />

was detected must be related to the reducing conditions present in Grimsel waters. The mobility<br />

of Re would be greatly affected if reduction to the oxidation state (IV) occurred.<br />

329

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