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                                                                                Chemical hydrogeology  79


































                   Fig. 3.4 Schematic diagram of the
                   evolution of groundwater along a
                   flowpath from recharge area to confined
                   section showing important hydrochemical
                   processes that affect the chemical
                   composition of groundwater. The
                   processes shown are not wholly sequential
                   in that ion exchange can occur without
                   substantial redox reactions (Section 3.9).


                   occur, highly saline waters or brines result (R →  and unsaturated zone, the dissolved CO produces
                                                                                                2
                   M/B in Fig. 3.3).                           a weakly acidic solution of carbonic acid, H CO ,
                                                                                                    2  3
                     In interpreting groundwater chemistry and identi-  which itself dissociates and promotes the dissolution
                   fying hydrochemical processes it is useful to adopt  of calcium and magnesium carbonates giving a Ca-
                   the concept of hydrochemical facies, or water type,  Mg-HCO water type. Away from the reservoir of
                                                                       3
                   introduced by Chebotarev (1955). A hydrochemical  oxygen in the soil and unsaturated zone, the ground-
                   facies is a distinct zone of groundwater that can be  water becomes increasingly anoxic below the water
                   described as having cation and anion concentrations  table with progressive reduction of oxygen, nit-
                   within definite limits. A pictorial representation of  rate and sulphate linked to bacterial respiration and
                   the typical changes in hydrochemical facies along a  mineralization of organic matter. Under increasing
                   groundwater flowpath is shown in Fig. 3.4. Dilute  reducing conditions, Fe and Mn become mobilized
                   rainwater with a Na-Cl water type and containing  and then later precipitated as metal sulphides (see
                   CO enters the soil zone, whereupon further CO ,  Section 3.9). In the presence of disseminated clay
                      2                                    2
                   formed from the decay of organic matter, dissolves in  material within the aquifer, ion exchange causes Ca 2+
                                                                                 +
                   the infiltrating water. Where relevant, the applica-  to be replaced by Na in solution and the water
                   tion of agricultural chemicals such as fertilizers add  evolves to a Na-HCO water type. In the deeper,
                                                                                 3
                           +  +   −   −       3−
                   further Na , K , Cl , NO and PO . Within the soil  confined section of the aquifer, mixing with saline
                                      3       4
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