Excess 234U: An aging effect in confined waters

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Abstract

Strong isotopic fractionation between234U and238U has been noted in deep oil-well brines. The waters are stratigraphically and structurally isolated from fresh-water inflow and have remained stagnant for more than five half-lifes of234U. Excess234U is explained by the234Th alpha-recoil nucleus event.

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    Where the uranium activity concentrations (or more commonly 234U/238U activity ratios) behave conservatively along groundwater flow paths variability can potentially identify inter-aquifer mixing, identify source waters and determine the relative proportions of source waters (Dabous and Osmond, 2001; Herczeg et al., 1996; Osmond et al., 1974; Paces et al., 2002; Paces and Wurster, 2014; Rosenthal and Kronfeld, 1982). Uranium isotope variations have also been used to determine groundwater flow rates by either the 234U excess decay model (Guttman and Kronfeld, 1982; Henderson et al., 1999; Kronfeld et al., 1975; Kronfeld and Rosenthal, 1981) or alternatively, by determining the progressive augmentation by aquifer processes (Ivanovich et al., 1991; Schaffhauser et al., 2014). Other groundwater studies found that U activities depended more upon the groundwater redox conditions (Andrews and Kay, 1983), radioelement distribution from diverse vadose zone inputs and weathering conditions (Kronfeld et al., 2004; Méjean et al., 2016; Post et al., 2017; Tricca et al., 2001), extent of water-rock interactions (Andrews et al., 1982) and stabilisation by the formation of uranium complexes (Herczeg et al., 1988; Jurgens et al., 2010).

  • Processes controlling <sup>234</sup>U and <sup>238</sup>U isotope fractionation and helium in the groundwater of the St. Lawrence Lowlands, Quebec: The potential role of natural rock fracturing

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    A detailed discussion on the helium isotopic systematics is beyond the scope of this paper and is reported in Vautour et al. (2015). Fig. 3 compares the measured [U] and (234U/238U)act in the current study area with those from other sedimentary aquifers characterized by similar lithologies and confinement conditions (except for confined oil brines; Kronfeld et al., 1975; Banner et al., 1990). Both measured [U] (Fig. 3a) and (234U/238U)act (Fig. 3b) from the study area are within the range of values observed in other unconfined and confined sedimentary aquifers (Banner et al., 1990; Bonotto and Andrews, 2000; Durand et al., 2005; Hubert et al., 2006; Reynolds et al., 2003; Riotte and Chabaux, 1999; Tricca et al., 2001), but are characterized by higher variability.

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    These mechanisms are favoured (Osmond and Cowart, 1992; Ivanovich et al., 1991) by long period of interaction between water of low dissolved uranium contents and hosting formations of relatively higher uranium concentrations. Several studies have reported activity ratios reaching 12 in large confined aquifers with steady long term system such as 9.0 for deeper and older shallow groundwater of the Transvaal Dolomite Aquifer in South Africa (Kronfeld et al., 1994), 10.1 for groundwater sampled from a deep well in Ramallah (Kronfeld et al., 1975), 10.5 in confined aquifers in the Cambrian and Ordovician bedrock in the tri-state region of Missouri, Kansas and Oklahoma (Cowart and Osmond, 1980), 11.8 at a redox front of the Milk River aquifer (Ivanovich et al., 1991) and 12.3 in a confined sandstone aquifer in Texas (Kronfeld, 1974). Activity ratios as high as 28 have also been observed in the brazilian part of the Guarani aquifer (Bonotto, 2006) and have been explained by the large extension of the system enhancing the three main factors responsible of uranium isotopes disequilibria (rock–water interactions, preferential chemical dissolution and alpha-recoil release of 234U).

  • Chapter 10 Uranium- and Thorium-Series Radionuclides in Marine Groundwaters

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    This application is based on the fact that 234U, unlike 238U, can be mobilized to sediment pore water via recoil of 234Th and subsequent decay of the 234Th. This process accounts for greater-than-unity 234U/238U activity ratios in terrestrial groundwaters (e.g. Hussain and Krishnaswami, 1980; Kronfeld et al., 1975; Hussain and Lal, 1986; Osmond and Cowart, 1992; Porcelli, this volume) and 234U/238U activity ratios in marine sediment pore waters that are elevated relative to the seawater value of 1.149 (Cochran and Krishnaswami, 1980; Maher et al., 2004). Maher et al. (2004, 2006) have used high-resolution mass-spectrometric measurements of U concentrations and 234U/238U ratios in sediment pore water to determine low-temperature bulk and mineral dissolution rates of sediment over time-scales of ∼500,000 ky.

  • Rates of silicate dissolution in deep-sea sediment: In situ measurement using <sup>234</sup>U/<sup>238</sup>U of pore fluids

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    Rocks and minerals maintain the equilibrium activity ratio of unity unless they have been disturbed recently by physical or chemical processes such as comminution or leaching; thus unlike other radiogenic isotope systems used in geochemistry, rocks are nearly uniform in 234U/238U. Fine-grained solids, however, do not quantitatively retain intermediate decay products of uranium because of α-recoil effects (Bonotto and Andrews, 1993; Fleischer, 1980, 1982a, 1988; Kigoshi, 1971; Kronfeld et al., 1975; Ku, 1965). The α-recoil effect causes the 234U/238U ratio of fine-grained solids (<∼250 μm in diameter) to depart from the equilibrium value resulting in excess 234U in the interstitial fluid phase.

  • Uranium series isotopes in the Avon Valley, Nova Scotia

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1

Present Address: Department of Geophysics and Planetary Sciences, Tel-Aviv University.

2

Permanent Address: Max-Planck-Institut für Kernphysik, Heidelberg.

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