Abstract

The hydrochemical response of fracture zones to enhanced recharge into the upper bedrock environment has been studied during a 3 a project at the Äspö Hard Rock Laboratory (HRL) in Southeastern Sweden. Hydrochemical data obtained during the experiment provides a basis for development of a model for the impact of accelerated recharge on groundwater composition and reactive processes during repository construction and operation. Tunnel construction at the HRL resulted in a 50-fold increase in recharge rates, and a 30-fold decrease in groundwater residence times in the fracture zone studied. Up to 80% dilution of the native groundwater created the greatest impact on groundwater composition. In addition, comparison of mass balances for solutes with known conservative behaviour, and reactive solutes, indicates a significant source of HCO − 3, SO 2− 4 and Na + ions and a significant sink for Ca 2+ ions within the fracture zone. These trends are explained by ion-exchange processes and microbial degradation of organic C transported from the soil with recharge. The increased microbial activity helps maintain anoxic conditions within the fracture zone. The enhanced recharge favours the performance of the geological barrier since anoxic conditions help to protect against corrosion of engineered barriers, and because long-lived isotopes of Np, Tc and U are less soluble under reducing conditions. A secondary impact is the strong dilution which affects trace element speciation, and also the stability and possible transport of colloids, through ion strength effects. Results from this experiment are primarily significant for national radioactive waste disposal programs that consider potential repository sites in granite geology, and for other programs considering disposal in fractured rock.

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