Page 168 - Geochemistry of Oil Field Waters
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ALUMINUM                                                             155

            Aluminum

              Aluminum is the third most  abundant element in the earth’s crust, but its
            concentration in natural waters usually is less than 1 mg/l. The ionic radius
            of  trivalent aluminum is 0.57 a (Goldschmidt, 1958), and it usually behaves
            as  a  cation  when  6-coordinated  with  oxygen  compounds.  However, when
            4-coordinated,  it  usually  acts  like  the  central  atom  of  an  anion.  The
            4-coordination  usually,  but  not  exclusively,  is  associated  with  minerals
            formed  at  high  temperatures,  but  the  6-coordination  is  associated  with
            minerals formed at low temperatures, which includes most sediments in the
            petroleum environment.
              The  clay  minerals  illite,  kaolinite,  and  montmorillonite  often  contain
            about  13.5,  21,  and  11% aluminum,  respectively.  Quartzites,  sandstones,
            limestones,  and  shales  contain  about  0.7,  3.0,  0.6,  and  10% aluminum,
            respectively.  During  weathering  silica  will  leach  out  and  leave aluminum
            hydroxide  behind  (Pirsson and  Knopf, 1947), and sedimentation processes
            leave only about 0.4 mg/l aluminum in sea water.
              According to Hem (1970), the cation AP3 predominates in solutions with
            a pH of  4.0  or less. Above pH 4.5, polymerization gives rise to an aluminum
            species with a gibbsite  (aluminum hydroxide) structural pattern.  Above pH
            7.0, the dissolved form is the anion A1 (OH),-.
              The pH of  the water is the main control of the amount of alumium that is
            likely to be present in natural waters.  A water with a pH  less than 4.0 may
            contain 1% or more of  aluminum; for example, waters associated with acid
            mine drainage. Oilfield waters contain trace amounts to more than 100 mg/l
            of aluminum.

            A 1 ha 1 in ity

              Alkalinity  is defined  as the capacity  of  a solution to neutralize an acid,
            usually  to a  pH  of  4.5.  A  solution  with  a  neutral  pH  of  7.0  may  have  a
            considerable amount of  alkalinity; therefore, alkalinity is a capacity function,
            in  contrast  to pH,  which is an intensity function. The alkalinity-pH ranges
            originally  coincided  with  methyl  orange  and  phenolphthalein  color  end
            points.  The  potentiometric  titration  produces  more  accurate  alkalinity
            results,  and it utilizes an end point where the most abrupt pH change occurs
            while specific increments of a standard acid are added.
              Alkalinity  usually is caused by the presence of  bicarbonate, carbonate, or
            hydroxyl ions in a water; however, the weak acids such as silicic, phosphoric,
            and boric can contribute titratable alkalinity species. Carbon dioxide, which
            is dissolved in  circulating waters  as bicarbonate or carbonate as a result of
            the carbon cycle, is the prime source of  alkalinity in shallow ground waters.
            However,  in  deep subsurface  brines,  additional carbon dioxide probably  is
            dissolved as a result of diagenesis of inorganic and organic compounds.
              Most oilfield waters contain no hydroxyl ions, and most of  them contain
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