An Improved Model For Determining Salinity Recharge Time for Deep Borehole Disposal - 20405
Creators
- 1. Deep Borehole Disposal Research Group, Immobilisation Science Laboratory, Department of Materials Science and Engineering, The University of Sheffield, Sheffield S1 3JD (United Kingdom)
Description
In a previous publication (K. P. Travis, D. Burley and F. G. F. Gibb, WM2017 Conference, Phoenix Arizona paper no. 17480) we introduced a numerical model to estimate the time it would take for a pressure perturbation to subside following its creation from the construction of a deep geological borehole in water-saturated rock. The model was based on the notion of a point source of momentum - a solution of the time-dependent pressure-diffusion equation. Using the model, we estimated that it would take on the order of 10 k years for physical equilibrium to become re-established following the sinking of a 5 km borehole in granite. The significance of such a model is that it places an upper bound on the lifetime required of a borehole sealing system - a necessary input to a borehole post-closure safety case assessment. No engineered sealing system has ever been devised which is capable of retaining its sealing properties for 10 half-lives of long-lived radioisotopes in spent fuel or high-level waste. One of the key advantages of disposing of nuclear waste via Deep Borehole Disposal (DBD) is the natural sealing provided by density stratified groundwater. Upon sinking of a borehole, and subsequent filling with fresh water, brine or drilling mud, this natural barrier may be temporarily damaged. Over time, fresh brine from the far-field will flow towards or away from the hole (driven by a pressure gradient) and will eventually re-establish the original salinity gradient. It follows that the engineered seals need last only as long as the time required for this salinity gradient to reset itself. One of the limitations of our previous model was the use of a static boundary condition on the borehole wall. The model used a boundary pressure which varied quadratically with depth (arising from differences between the pressure of a column of fresh water in the borehole and that of a column of brine in the host rock). However as brine replaces fresh water in the borehole (driven by a pressure gradient), the boundary function must change with time. We now introduce an improved model which takes this time dependent boundary condition into account. The model also takes into account the time taken for a mixture of brine and fresh water to re-establish chemical equilibrium through the process of diffusion. The paper contains the mathematical details of our new iterative model as well as results showing the time taken to reach steady state, and concentration profiles for the components of the brine-filled borehole as a function of time together with a discussion on the implications of the results for developing a post-closure safety assessment for DBD. (authors)
Availability note (English)
Available from: WM Symposia, Inc., PO Box 27646, 85285-7646 Tempe, AZ (US)Additional details
Identifiers
Publishing Information
- Imprint Pagination
- 30 p.
- Report number
- INIS-US--21-WM-20405
Conference
- Title
- 46. Annual Waste Management Conference
- Acronym
- WM2020
- Dates
- 8-12 Mar 2020
- Place
- Phoenix, AZ (United States)
INIS
- Country of Publication
- United States
- Country of Input or Organization
- France
- INIS RN
- 52068371
- Subject category
- S12: MANAGEMENT OF RADIOACTIVE WASTES, AND NON-RADIOACTIVE WASTES FROM NUCLEAR FACILITIES;
- Resource subtype / Literary indicator
- Conference, Non-conventional Literature
- Descriptors DEI
- BOREHOLES; BRINES; DIFFUSION EQUATIONS; DRILLING FLUIDS; FRESH WATER; GRANITES; GROUND WATER; GROUNDWATER RECHARGE; HIGH-LEVEL RADIOACTIVE WASTES; ITERATIVE METHODS; POINT SOURCES; PRESSURE GRADIENTS; RISK ASSESSMENT; SALINITY GRADIENTS; SPENT FUELS; STEADY-STATE CONDITIONS; TIME DEPENDENCE
- Descriptors DEC
- CALCULATION METHODS; CAVITIES; DIFFERENTIAL EQUATIONS; ENERGY SOURCES; EQUATIONS; FLUIDS; FUELS; HYDROGEN COMPOUNDS; IGNEOUS ROCKS; MATERIALS; NUCLEAR FUELS; OXYGEN COMPOUNDS; PARTIAL DIFFERENTIAL EQUATIONS; PLUTONIC ROCKS; RADIATION SOURCES; RADIOACTIVE MATERIALS; RADIOACTIVE WASTES; REACTOR MATERIALS; ROCKS; WASTES; WATER
Optional Information
- Notes
- 5 refs.; available online at: https://www.xcdsystem.com/wmsym/2020/index.html