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Patterns in groundwater                                               313


                       Recharge


                                                           Discharge


                                    Acid
                                           Temp
                               Polluted
                                       (Sub) oxic
                                                      Pressure  admixing
                                                     decrease
                                     Basic
                                 Acid exchange
                                                             Increased
                                         Anoxic
                                Unpolluted
                                           + pressure increase
                            Strong quality fluctuations
                                     Equillibrium
                                             Methanogenic
                                          Base-exchange
                                                                     6642  6642  6642
                                   Constant quality
                   Figure 17.4  Development of hydrochemical facies in the direction of groundwater flow  (after Stuyfzand, 1999).
                   4.   From oxic  to anoxic –methanogenic conditions due to the oxidation of organic matter
                      in a system closed from the atmosphere. This process brings about a typical order of
                      consumption of oxidants  (see Section 4.3.4; Figure 4.10) in water and an increase in
                      alkalinity  .
                   5.   From low to elevated pressure and water temperature  due to downward migration of
                      groundwater in groundwater recharge  areas. In groundwater discharge  areas the reverse
                                                                               2+
                                                                       +
                      occurs. An increase of temperature and pressure may lead to K  and Mg  depletion due
                      to recrystallisation of clay minerals  and to an increase of overall salinity due to a decrease
                      of the cation exchange capacity  .
                   Along the groundwater flow lines, substance concentrations can vary by up to several orders
                   of magnitude, due to differences in chemical inputs or the chemical processes. Towards the
                   groundwater discharge  areas, the groundwater flow  lines converge and the stream tube s
                   become narrower and increasingly mixed.
                      Figure 17.5 illustrates in more detail the concept of the hydrochemical development of
                   groundwater, using as an example the largely unconfined chalk  aquifer of  Dorset, southern
                                                                                        -
                   England (Edmunds and Shand, 2008a). Here, the background concentrations of Cl  are
                   controlled by rainwater chemistry after allowing for evapotranspiration and decline gradually
                   inland from the coast. The deepest part of the aquifer is separated from present-day groundwater
                   circulation, and in some parts minor residual salinity derived from older saline water may be
                   present. The major control on the composition of groundwater, however, is the geochemistry of
                   the chalk sediment. Interactions between groundwater and the chalk produce relatively alkaline,
                                               -
                                     2+
                   hard water, rich in Ca  and HCO  ions. Variations in the natural groundwater composition
                                              3
                   also take place with increasing residence time, a major cause being redox changes occurring as
                   groundwater moves beneath the Tertiary confining cover. In this deeper part of the chalk aquifer,
                                                    2+
                                            2+
                   high natural concentrations of Fe  and Mn  may be found (Edmunds and Shand, 2008a).
                      The above description of the development of groundwater composition demonstrates
                   that, as with soils, bedrock  geology is a major factor that controls the variation in the natural
                   composition of groundwater. The  potassium concentrations in European  bottled water as
                   shown in Figure 17.6 (Reimann and Birke, 2010) provide an illustrative example of the effect









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