Page 221 - Geochemistry of Oil Field Waters
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208                                         ORIGIN OF OILFIELD WATERS


            organic life (Baas Becking et al.,  1960). Because COz is the main byproduct
            of  organic  oxidation and the building material  of  plant and  much bacterial
            life,  it  plays a dominant role.  Carbon dioxide dissolves in water, producing
            the  bicarbonate  ion  and  a  free  hydrogen  ion.  The  concentration  of  the
            hydrogen  ion  is  lo-’  equiv./l  (pH  7) at  2OoC in  pure  water,  but  when
            saturated with  COz it rises to lo-’  (pH 5). This reaction moves to the right
            with  increasing  temperature  in  a  closed system.  In the presence of  organic
            constituents, the equilibrium is modified, and the pH range can extend from
            2 to 12.
              The ionic potentials of  the constituents involved in diagenesis are impor-
           tant (Cloke, 1966). Those that stay in true ionic solution up to rather high
            pH  levels are Na+, K+, Mg+’,  Fe+’,  Mn+2, Ca+’,  Sr+’, Ba+’, etc.; they are
           the soluble cations, and their ionic potentials range from 0 to 3, where the
           ionic  potential  is the  ratio  between  the  ionic  charge  and  the ionic radius.
            Constituents that are precipitated  by  hydrolysis are those with ionic poten-
           tials  from  3  to 12 and  include  such  ions  as  AP3, Fe+3, SP4, and
            Constituents that form soluble complex ions and usually go into true ionic
           solution include B+  3, V4, N+ ’, P+’ , S6, and Mn+’ ; their ionic potentials
           are  over  12. In general, the hydroxides of  the soluble cations possess ionic
           bonds; therefore, they are soluble, the hydrolysates or those precipitated by
           hydrolysis form  hydroxyl bonds, and the soluble complex  ions have hydro-
           gen bonds.
              Organisms that consume oxygen cause a lowering of  the redox potential,
           and  in  buried  sediments  it is the  aerobic  bacteria  that  attract  the organic
           constituents  and  remove  the free  oxygen  from  the interstitial  water.  Sedi-
           ments laid down in a shoreline environment  often differ in degree of  oxida-
           tion  from  those  laid  down  in  a  deep-sea  environment  (Pirson,  1968). For
            example,  the  Eh  of  the shoreline sediments may range from -50  to 0 mV
            while the Eh of  deep-sea sediments may range from -150  to -100  mV. The
            aerobic  bacteria  die  when  the  free  oxygen  is  totally  consumed,  and  the
            anaerobic bacteria  attack the sulfate ion which is the second most important
            anion  in  the sea  water.  During this attack, the sulfate is reduced to sulfite
            and  then  to sulfide.  Also  the Eh  drops to -600  mV  (Fig.7.2).  Sulfide  is
            liberated and CaC03 precipitates as the pH  rises above 8.5 (Dapples, 1959).
            Sulfur has two  stable isotopes,  * S and   S, with a mass differential of 6%.
           The isotopes are fractionated during the change of  S04-2  to Sv2, and SZ
           is  enriched  in  the  more  energetic 32S isotope. The average ratio of  3zS/34S
            in  normal sea water  sulfate is about 21.76 (Ault, 1959). The sulfate isotopes
           are useful in interpreting ancient diagenetic stages.
              Reactions occur during sediment diagenesis and affect the composition of
           the  interstitial  water.  Calcite  is  precipitated  if  the  pH  is  high,  or it is dis-
           solved if the pH is low. Dolomitization occurs as follows:

              2CaC03 + MgClz * CaMg(C03)2 + CaClz
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