Journal of Geochemical Exploration 89 (2006) 170 – 173 www.elsevier.com/locate/jgeoexp Bromine and stable isotopic profiles of formation waters from potash mine-shafts, Saskatchewan, Canada G.K.S. Jensen a,⁎, B.J. Rostron a , M.J.M. Duke b , C. Holmden c a Department of Earth and Atmospheric Sciences, University of Alberta, Edmonton, AB, Canada T6G 2E3 b SLOWPOKE Nuclear Reactor Facility, University of Alberta, Edmonton, AB, Canada, T6G 2E3 c Geological Sciences, University of Saskatchewan, Saskatoon, SK, Canada, S7N 5E2 Received 16 August 2005; accepted 24 November 2005 Available online 20 March 2006 Abstract Sixty-five inflow samples from access shafts were collected at three separate potash mines in order to construct three 1000 m deep hydrochemical profiles. Bromine concentrations, and δD and δ18O stable isotopic compositions, increase with depth in each case. Measured isotopic ratios have not changed in 15+ years since the mine-inflows were first sampled, implying little change in the hydraulic regimes at the mines over time. However, the bromine concentrations are typically a factor of five lower than previously reported. Newer analytical techniques have improved the accuracy, precision and resolution of the hydrochemical profiles. Results indicate that the salinity of the inflow waters originated as mixtures of evaporatively concentrated seawater, meteoric water, and brine derived from halite dissolution. Extremely concentrated brines (TDS N 525 g/L) were found at the Cory and Allan potash mines some 55 km apart, but their role in the paleohydrogeology of the basin remains uncertain. © 2006 Elsevier B.V. All rights reserved. Keywords: Potash; Brine; Isotopes; Bromide 1. Introduction The Prairie Evaporite Formation in the Elk Point Basin in Saskatchewan, Canada contains some of the largest deposits of potash in the world. Problematic mine-level flooding has threatened the longevity of potash mines in Saskatchewan almost since their construction (Wittrup et al., 1987). Therefore, it is essential to determine the origin of inflows to remediate them or to plan preventative maintenance. Previously, hydrochemical tracers such as chloride or major ions have had ⁎ Corresponding author. E-mail address: [email protected] (G.K.S. Jensen). 0375-6742/$ - see front matter © 2006 Elsevier B.V. All rights reserved. doi:10.1016/j.gexplo.2005.11.071 limited success because the inflows pass through, and dissolve, evaporites of the Prairie Evaporite Formation. Isotopic tracers (e.g., δ18O, δD) have met with more success at fingerprinting waters in the potash mines (Wittrup et al., 1987; Wittrup and Kyser, 1990) and oil fields in the basin (Rostron and Holmden, 2000). In addition, bromine has worked well in oilfield applications (Iampen and Rostron, 2000), however, the application of bromine in potash mine-inflow fingerprinting was hampered by analytical interferences. A recently developed analytical technique using Epithermal Neutron Activation Analysis (ENAA) for determining bromine concentrations in brines (Duke and Rostron, in press) facilitates the re-examination of G.K.S. Jensen et al. / Journal of Geochemical Exploration 89 (2006) 170–173 Fig. 1. Location of the sampled potash mines. bromine as a tracer for fingerprinting inflows in potash mines. That, combined with newer continuous flow stable isotope methods that allow measurements on small (b 5 mL) samples, and the more than 15+ year elapsed time since the pioneering fingerprinting work by Wittrup and Kyser (1990), prompted a re-examination of the chemistry of the inflows into potash mine shafts in Saskatchewan. Thus, the primary objective of this study was to obtain new hydrochemical and stable isotope vertical-profiles at the Potash Corporation of Saskatchewan (PCS) Rocanville, Cory, and Allan potash mines in Saskatchewan (Fig. 1), and to compare these results to previously published data. 2. Methods Sixty-five inflow samples from access shafts were collected at three separate mines (Fig. 1) in order to construct three 1000 m deep hydrochemical profiles for each mine. Sample points were identified by visual identification of water seeping into the dry mine shafts. Samples were collected into sealed plastic containers, and the depth below ground was calculated from the amount of cable dispensed to support the elevator car. 171 Field filtration was done using 0.45 μm PES filters to remove any suspended solids. Oxygen and hydrogen stable isotopes were determined at the University of Saskatchewan. An aliquot of brine was injected directly into a continuous flow (CF) Delta plus XL isotope ratio mass spectrometer. Isotopic values were reported in delta (δ) notation as 18O/16O and D/H relative to Vienna Standard Mean Ocean Water (VSMOW). Isotopic measurements have an uncertainty of ± 3‰ and ± 0.3‰ for δD and δ18O, respectively. ENAA was completed at the SLOWPOKE Reactor at the University of Alberta to determine the sodium, chloride, bromide and iodine concentrations of each sample. Bromide concentrations varied from 17.9 to 6520 mg/L with uncertainties ranging from ± 3.9% and ± 0.6%, for this concentration range. Ion chromatography was not used for bromide analysis as a dilution factor of ∼10,000 would have been required, due to the high TDS contents of the samples. Major ions, trace metals, and alkalinity data were determined at a commercial laboratory in Edmonton, Alberta using ICP-OES, ICP-MS, and titration techniques. Analytical uncertainties for the commercially determined ions varied with the different techniques, and details are available upon request of the authors. 3. Results and discussion Each of the 65 samples collected for this study were fully analyzed for their major and minor ion and isotopic composition. Space limitations preclude a display and discussion of most of these data, instead, a comparison between data collected previously by Wittrup et al. (1987) and the newly collected data is provided. The two most important parameters are the bromine and stable isotopic compositions of the potash shaft inflows. Bromine concentrations versus depth for the Cory, Allan, and Rocanville potash mines are shown in Fig. 2. Bromine increases with depth at all three mines and Fig. 2. Bromine concentrations versus depth for Cory, Allan and Rocanville potash mines. Note that bromine is a logarithmic scale. 172 G.K.S. Jensen et al. / Journal of Geochemical Exploration 89 (2006) 170–173 Fig. 3. δD (VSMOW) versus depth for Cory, Allan and Rocanville potash mines. range from approximately 2 mg/L in near-surface aquifers (58 m depth), to a maximum of approximately 5500 mg/L in Devonian carbonate aquifers (1025 m depth) just above the mining horizon. Inflow samples with bromine concentrations of 5500 mg/L are found at the Cory and Allan mines some 55 km apart. These calcium-chloride brines are the most concentrated waters found in the Williston basin to date, with total dissolved solids of 525,000 mg/L. They contain elevated chloride (350,000 mg/L), calcium (136,000 mg/L), and magnesium (22,000 mg/L), yet relatively low sodium (6400 mg/L) and their widely spaced nature implies that they are more than just an isolated occurrence at each mine. The origin and implication of these extremely bromine-rich brines is the subject of on-going research. There are significant differences between the newly determined bromine profiles and those previously published. Firstly, there are more samples in these new profiles because the analytical techniques require less sample (i.e. 0.25 mL), hence smaller inflows can be analyzed. This gives our new profiles a finer resolution. Secondly, at any given depth the bromine concentrations in this study are significantly lower than measured in the previous study, with the difference becoming larger at greater depths, that is, higher concentrations. This difference is attributed to the analytical method by Wittrup et al. (1987) (ion selective electrode) being affected by interference with increasingly high chloride concentrations with depth increases. In some cases the bromine concentrations obtained using ENAA in this study were an order of magnitude less than previously determined. Thirdly, samples with such elevated bromine (N5000 mg/L) were not previously reported at the Allan mine. Isotopic compositions of the mine inflows are illustrated by means of plots of δD versus depth for each mine (Fig. 3). Isotopic compositions of δ18O are not shown because they follow a similar pattern to δD and previous work has demonstrated a linear relationship between δD and δ18O for the Williston Basin (Wittrup and Kyser, 1990). At all three mines, δD compositions in the mine inflows increase with depth (Fig. 3). At shallow depths, water samples have an isotopic composition (− 160 ‰) similar to that of meteoric water in Saskatchewan (Wittrup et al., 1987). At the greatest depths in the mines, isotopic compositions in Devonian strata reach − 45‰, similar to that reported previously (Wittrup and Kyser, 1990; Rostron and Holmden, 2000). Variations in the isotopic compositions of the inflows as a function of depth are interpreted to reflect differences caused by the origin and/or mixing history of the fluids in different aquifers at each level of the shaft. Using these data, an isotopic fingerprint has been obtained for the aquifers above the mine providing excellent tracers of the origin (s) of the shaft inflows. Current isotopic compositions versus depth compare very closely to those published previously (Wittrup et al., Fig. 4. Na / Br versus Cl / Br (mg/L) of shaft inflow samples. G.K.S. Jensen et al. / Journal of Geochemical Exploration 89 (2006) 170–173 1987; Wittrup and Kyser, 1990), with a few differences. Firstly, as mentioned above, these isotopic profiles of this study are more detailed than previously shown as a result of an increased number of samples made possible by the CF analytical techniques. Continuous flow can measure the isotopic composition on small (b2 mL) brine samples, and thus small shaft inflows can be included in the vertical profiles. This has resulted, for example, in data for the deep aquifers above the Cory and Allan mines (Fig. 3A, B) and in other places in the profiles that were not available previously. Secondly, with the exception of data from 600 to 800 m in Rocanville mine, the isotopic data from 1987 overlap those collected in this study. This indicates there has been no change over time in the isotopic composition of the shaft inflows. Observed differences in isotopic compositions at the Rocanville mine are attributed to sample collection at or near pumping stations where inflows are collected for pumping to the surface, and hence are not considered representative. 4. Origin of formation water Revised bromine concentration data from the 3 mine shafts provide additional insight into the origin of the formation waters in the basin. A plot of Na / Br vs. Cl / Br (Fig. 4) illustrates a linear relationship in the data but with a wide variation compared to seawater. Variations in the Na / Br ratios of the samples can be used to infer the origin of the salinity in the samples (Walter, 1990). Samples from Rocanville all plot above and to the right of seawater on the Na / Br vs. Cl / Br plot, indicating the salinity in these samples originated from the dissolution of halite. In contrast, samples from Cory and Allan, plot over a wide range on the Na/Br vs. Cl/Br plot, both above and to the right of seawater (indicating dissolution of halite) and below and to the left of seawater indicating the presence of an evaporated end-member brine. Samples with Br N 5000 mg/L found above the potash mining horizon at Cory and Allan are thought to represent the evaporated end-member brine. As mentioned above, the recognition of the evaporatively concentrated end-member brine at the Allan potash mine, and the fact that it is 173 found 55 km away from the previously known occurrence at the Cory mine, suggests that this formation water is more widespread than previously known. This indication bears further investigation. 5. Conclusions Sixty-five samples of inflows into access shafts at PCS Cory, Allan, and Rocanville potash mines were analyzed and used to construct hydrochemical profiles through the aquifers in the Williston Basin. There have been no significant change in the isotopic compositions of the shaft inflows in the 15+ years since they were initially studied, indicating that the origin of the inflows have not changed. Newer analytical techniques for both bromine (ENAA) and stable isotopes (CF) enabled the analysis of smaller samples than in previous studies in creation of higher resolution depth profiles which were both more accurate and precise for bromine. Sampling identified an evaporatively concentrated brine at the Allan mine, previously only recorded at the Cory mine. In addition to stable isotopes of oxygen and hydrogen, bromine concentration data can be used to better define the source of mine-level flooding brines. References Duke, M.J.M., Rostron, B.J. Determination of bromine, iodine, chlorine and sodium in highly saline formation waters by Epithermal NAA, Journal of Radioanalytical and Nuclear Chemistry. Iampen, H.T., Rostron, B.J., 2000. Hydrochemistry of pre-Mississippian brines, Williston Basin, Canada–USA. Journal of Geochemical Exploration 69–70, 29–35. Rostron, B.J., Holmden, C., 2000. Fingerprinting formation-waters using stable isotopes, Midale Area, Williston Basin, Canada. Journal of Geochemical Exploration 69–70, 219–223. Walter, L., 1990. Br–Cl–Na systematics in Illinois basin fluids: constraints on fluid origin and evolution. Geology 18, 315–318. Wittrup, M.B., Kyser, T.K., 1990. The petrogenesis of brines in Devonian potash deposits of western Canada. Chemical Geology 82, 103–128. Wittrup, M.B., Kyser, T.K., Danyluk, T., 1987. The use of stable isotopes to determine the source of brines in Saskatchewan potash mines. Economic Minerals of Saskatchewan. Special Publication, vol. 8. 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