water releases NH4+ and I- ions from entrained
organic matter (e.g., Sholkovitz 1995). The main
sources of the elements in mineral waters are Cl-rich
fluids of a different origin, rock dissolution and
dissolved gases (CO
2
) (Chelnokov et al. 2018). It is
well known that the presence of dissolved CO2
enhances the extent of water-rock interactions,
particularly at the low temperature. Therefore,
associated CO2 gas increases the water-rock
interactions and more intensely leaches elements
from the bedrock. Thermodynamic calculations
indicate that all mineral waters are oversaturated
relative to the primary aluminosilicate minerals
(SIalbite =1.2–2.8), quarts (SIquartz =0.4–1.2),
hydroxides (SIhematite =9.2–17) and carbonate
minerals (SIcalcite =0.2–1.4).
The studied waters had not been analysed
previously with regard to rare earth elements content.
Typical for borehole №33 maximal concentrations
of total REE are almost two times higher than in the
bh № 22 and are remarkably higher than in other
boreholes (Table 1). The minimal concentrations
show fresh groundwaters (bh №8F). To more
conveniently view inter-element trends, the REE
analyses have been normalized to North American
Shale Composite (Gromet et al. 1984). The NASC-
normalized patterns of groundwaters are
characterized by HREE enrichments and positive Eu
anomalies. The interesting difference consists in Ce
anomaly: some fluids are characterized by positive
Ce anomaly (Ce/Ce*=1.1-5.4) (bh № 33, 22, 963)
(Figure 2A) and others have moderate negative Ce
anomaly (Ce/Ce*=0.5-0.6) (bh № 16, 17, 18)
(Figure 2B). Anomalies of Ce were of particular
interest following the ano maly’s potential use as an
indicator of water/rock interaction processes or as a
hydrological tracer (Seto and Akagi 2008).
The positive Eu-anomalies are common for both
groups and are likely reflecting weathering reactions
with host rocks as a result of the preferential
dissolution of a Eu-rich phase (e.g. plagioclase).
Other way groundwater might reflect considerably
more reduced conditions (De et al. 1988; Sholkovit z
1995). Also the Eh conditions of the waters could
specify the difference in Ce anomalies. It is known
that negative Ce anomalies require near-surface
partitioning of Ce due to the oxidation of Ce
3+
to
Ce
4+
and precipitation under oxidative conditions
(Eh>0) (Johannesson et al. 1997; Lewis et al. 1997).
negative Ce anomalies do not occur in reduced
fluids (Eh<0) since Ce
3+
doesn’t oxidize to Ce
4+
.
Also it can be explained by regional bedrock
mineralogy and lithology (Ce-depleted source
minerals in the materials through which the water
flows). Experimental data (Bau, 1999) indicate that
variation in Ce anomaly magnitude could be a result
of the difference in residence time of groundwater
circulation. It is in a good agreement with behavior
of Ce: in boreholes which are being operated (№ 16,
17, 18) we observe Ce minimum and unused
boreholes (№ 963, 22, 33) have Ce maximu m.
The explanation for the HREE-enriched pattern
is that the HREEs form stronger complexes with
ligands in solution than do the LREE. This has two
consequences: the HREEs will be preferentially
released to solution during weathering of source
rocks; and the LREE will be preferentially adsorbed
at particle surfaces in adsorption/equilibria reactions
in waters. The presence of CO
2
gas also enhances
the concentration of heavy REE (Kharitonova et al.
2007). Results of major and trace elements of bulk
mineral precipitates are given in Table 2. The
samples from the top of the well were limpid, white
salt crystals.
The Al
2
O
3
and Na
2
O contents of the sample are
consistently very high (~35%) and (~10%)
correspondingly. Mineral precipitates are enriched
with LREE (89%) compared to the HREE (11%), it
is in good correlation with mineral water producing
this precipitates (Bh №16) containing LREE -79%
and HREE -21% (Tables 1, 2). Comparing the rare
earth element signature of waters with its mineral
precipitates reveals differences (Figure 2). NASC-
normalized concentrations are higher for REE in
solid phase than for the water. The respective
NASC-normalized REE pattern decreases slightly
from La to Nd, increases from Eu to Lu; and shows
a small positive Ce and negative Eu anomalies
(Table 2). Enrichment of Ce in solid phase (Bh №16
Ce/Ce*= 1.2) is clearly indicated by the depletion of
this element in corresponding waters (Bh №16
Ce/Ce*= 0.6). Positive Ce anomaly can indicate
redox controlled processes leading to the formation
of CeO
2
(Aubert et al. 2001). Whereas Eu do not
accumulate in mineral precipitates and demonstrates
lowest level among REE (Table 2, Figure 2B).
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