Environmental Impact of Underground Construction From a Hydrological and Hydrochemical Disturbance Perspective
- Fredrik Mossmark (Geological Survey of Sweden) | Lars O. Ericsson (Chalmers University of Technology) | Anders Blom (Sweco Environment AB)
- Document ID
- International Society for Rock Mechanics and Rock Engineering
- ISRM International Symposium - 10th Asian Rock Mechanics Symposium, 29 October - 3 November, Singapore
- Publication Date
- Document Type
- Conference Paper
- 2018. International Society for Rock Mechanics and Rock Engineering / Society for Rock Mechanics and Engineering Geology
- Tunneling, Groundwater, Hydrogeochemistry
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- 7 since 2007
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In most projects involving underground construction, impact to hydrogeological conditions is monitored through measurements of groundwater levels. In contrast, hydrological and hydrochemical changes are rarely monitored throughout a project and the assessment of environmental resilience is often limited to an evaluation that broadly links the behavior of groundwater levels with a large number of engineering geological and ecological parameters.
An ongoing field research project in Sweden is based on monitoring the recovery of hydrogeological, hydrological and hydrochemical conditions after a long-term groundwater extraction. The groundwater discharge was intended to simulate effects of underground construction. Groundwater was extracted during a period of five years from fractured igneous rock in a previously glaciated area with thin soil cover. During this time the hydrogeological and hydrological conditions were altered with lowered groundwater levels and the surface runoff from the area decreased by nearly 50%. Meanwhile significant hydrochemical changes were observed with spikes in sulfate and lowered pH in groundwater as well as in surface water.
Preliminary results show that hydrological recovery after the groundwater extraction took more than three years, despite apparent quick recovery of groundwater levels with runoff volumes remaining lower than in a nearby reference area. Meanwhile, hydrochemical conditions did not return to those that existed prior to groundwater extraction. During the first three years of recovery, sulfate remained higher in shallow groundwater bodies, whereas base cations were lower compared to before the extraction started. After ten years of recovery sulfate concentrations have decreased by 30% to 60%, in both surface water and groundwater bodies, whereas chloride concentrations have increased compared to before the extraction. By restricting monitoring to only groundwater levels, some environmental impacts due to underground constructions may be missed.
Underground constructions are generally subjected to groundwater leakage (Gustafson 2012), and the implications of this have been studied in several underground constructions. Romeriksporten in Norway (Kitter⊘d et al. 2000; Kvӕrner and Snilsberg 2013), the Hsueh-Shan Tunnel in China (Chiu and Chia 2012), the Hallandsås rail tunnels (Mossmark et al., 2017), the Kattleberg rail tunnels (Mossmark, 2015) and the Bolmen Tunnel in Sweden (Olofsson 1991) are examples of particularly well documented tunnelling projects from a groundwater perspective.
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