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Biogeochemical processes in a clay formation in situ experiment: Part A - Overview, experimental design and water data of an experiment in the Opalinus Clay at the Mont Terri Underground Research Laboratory, Switzerland
Authors:P. Wersin,O.X. LeupinS. Mettler,E.C. GaucherU. Mä  der,P. De Canniè  reA. Vinsot,H.E. Gä  blerT. Kunimaro,K. KihoL. Eichinger
Affiliation:a NAGRA, Hardstrasse 73, 5430 Wettingen, Switzerland
b BRGM, 3 avenue Claude Guillemin, B.P. 36009, 45060 Orléans Cedex 2, France
c University of Bern, Institute of Geological Sciences, Baltzerstrasse 3, CH-3012 Bern, Switzerland
d SCK·CEN, Waste and Disposal Project, Boeretang 200, 2400 Mol, Belgium
e ANDRA, Laboratoire de Recherche Souterrain de Meuse/Haute-Marne, RD960 BP9, 55290 Bure, France
f BGR, Stilleweg 2, 30655 Hannover, Germany
g JAEA, Tokai-mura, Naka-gun, Ibaraki 319-1195, Japan
h CRIEPI, 1646 Abiko, Abiko-city Chiba 270-1194, Japan
i Gruner Ltd., Gellertstrasse 55, 4020 Basel, Switzerland
j Solexperts Ltd., Mettlenbachstrasse 25, 8617 Mönchaltorf, Switzerland
k Hydroisotop, 85301 Schweitenkirchen, Germany
Abstract:An in situ test in the Opalinus Clay formation, termed porewater chemistry (PC) experiment, was carried out for a period of 5 years. It was based on the concept of diffusive equilibration whereby a traced water with a composition close to that expected in the formation was continuously circulated and monitored in a packed-off borehole. The main original focus was to obtain reliable data on the pH/pCO2 conditions of the porewater, but because of unexpected microbiologically-induced redox reactions, the objective was extended to elucidate the biogeochemical processes occurring in the borehole and to understand their impact on pH/pCO2 and porewater chemistry in the low permeability clay formation.The behaviour of the conservative tracers 2H and Br could be explained by diffusive dilution in the clay and moreover the results showed that diffusive equilibration between the borehole water and the formation occurred within about 3 year’s time. However, the composition and pH/pCO2 conditions differed considerably from those of the in situ porewater. Thus, pH was lower and pCO2 was higher than indicated by complementary laboratory investigations. The noted differences are explained by microbiologically-induced redox reactions occurring in the borehole and in the interfacial wall area which were caused by an organic source released from the equipment material. The degradation of this source was accompanied by sulfate reduction and - to a lesser extent - by methane generation, which induced a high rate of acetogenic reactions corresponding to very high acetate concentrations for the first 600 days. Concomitantly with the anaerobic degradation of an organic source, carbonate dissolution occurred and these processes resulted in high pCO2 and alkalinities as well as drop in pH. Afterwards, the microbial regime changed and, in parallel to ongoing sulfate reduction, acetate was consumed, leading to a strong decrease in TOC which reached background levels after about 1200 days. In spite of the depletion of this organic perturbation in the circuit water, sulfate reduction and methanogenesis continued to occur at a constant rate leading to near-to-constant concentrations of sulfate and bicarbonate as well as pH/pCO2 conditions until the end of the experiment. The main sink for sulphur was iron sulfide, which precipitated as FeS (am) and FeS2.The chemical and isotopic composition was affected by the complex interplay of diffusion, carbon degradation rates, mineral equilibria and dissolution rates, iron sulfide precipitation rates, and clay exchange reactions. The 13C signals measured for different carbon species showed significant variations which could only be partly explained. The main cations, such as Na, Ca and Mg remained remarkably constant during the experiment, thus indicating the strong buffering of the formation via cation and proton exchange as well as carbonate dissolution/precipitation reactions.
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