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Ninth International Conference on Permafrost ... - IARC Research

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Deep <strong>Permafrost</strong> Studies at the Lupin Mine:Hydrogeological and Geochemical Informati<strong>on</strong> for Nuclear Waste DisposalLasse Ah<strong>on</strong>enGeological Survey of FinlandTimo RuskeeniemiGeological Survey of FinlandRandy StotlerUniversity of Waterloo, CanadaShaun FrapeUniversity of Waterloo, CanadaKimmo LehtoPosiva Oy, FinlandIgnasi PuigdomenechSKB (Swedish Nuclear Fuel and Waste Management Co), SwedenM<strong>on</strong>ique HobbsNuclear Waste Management Organizati<strong>on</strong>, CanadaPaul DegnanNirex, UK (present positi<strong>on</strong> CSIRO Explorati<strong>on</strong> & Mining, Australia)Introducti<strong>on</strong>The deep geological disposal of high-level and l<strong>on</strong>g-livednuclear waste requires a comprehensive understanding ofthe possible impacts of l<strong>on</strong>g-term future climate change <strong>on</strong>a repository envir<strong>on</strong>ment and the surrounding rock mass.Despite the general scientific c<strong>on</strong>sensus that global warmingis underway due to anthropogenic greenhouse gas emissi<strong>on</strong>s,future glaciati<strong>on</strong> scenarios have to be taken into accountand included in the l<strong>on</strong>g-term safety analyses of disposalsystems, especially in Fennoscandian countries, Britain, andCanada.The Lupin gold mine, situated in the territory of Nunavut,Canada, is located in a subarctic tundra envir<strong>on</strong>ment,where c<strong>on</strong>tinuous permafrost reaches depths of 400–600m. The bedrock of the Lupin area c<strong>on</strong>sists of Archeanmetasedimentary crystalline rocks, which are c<strong>on</strong>sideredto be good analogues for host rocks at potential repositorysites in the Fennoscandian Shield. C<strong>on</strong>sequently, severalnuclear waste management organizati<strong>on</strong>s, together withthe Geological Survey of Finland and the University ofWaterloo, started a joint venture to study the hydrogeologicaland hydrogeochemical c<strong>on</strong>diti<strong>on</strong>s below and within thepermafrost at the Lupin mine (Ruskeeniemi et al. 2003).Several important uncertainties relating to the potentialeffects of permafrost <strong>on</strong> the safety of nuclear waste disposalwere identified as follows:• Depth range and rate of formati<strong>on</strong> of permafrost incrystalline rock and the c<strong>on</strong>trolling factors.• Hydrogeological c<strong>on</strong>diti<strong>on</strong>s in frozen rock, theimportance of taliks as possible flow paths and thefreezing of water in major fracture z<strong>on</strong>es.• Hydrogeochemical effects of permafrost, formati<strong>on</strong>of saline segregati<strong>on</strong>s (cryopegs) in and/or below thefrozen rock mass.• Methane hydrates, the abundance and formati<strong>on</strong> ofmethane in crystalline rock and the nature of anyaccumulati<strong>on</strong>s below the permafrost.<strong>Research</strong> ActivitiesThe research project at the Lupin mine was c<strong>on</strong>ductedin three phases. During the first phase, background data <strong>on</strong>geology and hydrology were compiled, potential fracturez<strong>on</strong>es were identified by a seismic refracti<strong>on</strong> study, andunderground waters were sampled (Ruskeeniemi et al.2002). Phase II activities included an electromagnetic survey(SAMPO), drilling of two research boreholes from insidethe mine upwards through the bottom of the permafrost,water and gas sampling, crush and leach studies of therock material, and freezing experiments of water samples(Ruskeeniemi et al. 2004, Frape et al. 2004).Phase III (Stotler et al. 2008) focused <strong>on</strong> the collecti<strong>on</strong>of representative data c<strong>on</strong>cerning the chemistry and isotopiccompositi<strong>on</strong> of waters and dissolved comp<strong>on</strong>ents frompacked-off boreholes, the l<strong>on</strong>g-term m<strong>on</strong>itoring of hydraulicheads in the boreholes, mineralogical studies of fracturedrock, and a ground penetrating radar survey.Hydrogeological C<strong>on</strong>diti<strong>on</strong>sIn the mine, the bedrock below the permafrost down toabout 900 m appeared distinctly dry, as observed al<strong>on</strong>g theramp roadway. Mine statistics indicate pumping rates ofabout 6 m 3 /h (in 2003), of which a major proporti<strong>on</strong> wasidentified to be fresh water supplied for various purposes inthe mining process. Most of the water-producing boreholessituated at the level 1130 m were plugged. At higher levelsthe seepage of groundwater through frozen bedrock does notappear to take place at all. Measured effective porosities of1

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