Page 182 - Geochemistry of Oil Field Waters
P. 182

PHYSICAL PROPERTIES                                                  169


            Fig. 5.19 can be used to predict that ferrous ions are the more common form
            of  dissolved iron and that ferric ions will precipitate in an oxidizing environ-
            ment  if  the  pH  is  above  1. Similar  diagrams  can  be  drawn  for other con-
            stituents.
              Some water associated  with petroleum is “connate”  water, and Fig. 5.19
            indicates that such water has a negative Eh; this has been proven  in various
            field  studies  (Buckley et al.,  1958). The  Eh  of  some petroleum-associated
            waters in the Anadarko  Basin ranged  from -270  mV to -300  mV (Collins,
            1969a).
              Knowledge of  the Eh is useful  in determining how to treat a water before
            it is injected into a subsurface formation  (Ostroff, 1965). For example, the
            Eh of  the water will be oxidizing if  the water is open to the atmosphere, but
            if  it is kept in a closed system in an oil-production operation, the Eh should
            not change appreciably as it is brought to the surface and then reinjected. In
            such  a  situation,  the  Eh value is useful  in determining how much iron will
            stay in solution and not deposit in the well bore.
              Organisms that consume oxygen  cause a lowering of  the redox potential.
            In  buried  sediments,  it  is  the  aerobic  bacteria  that  attract  organic  con-
            stituents  which  remove  the  free  oxygen  from  the  interstitial  water.  Sedi-
            ments laid down in a shoreline environment will differ in degree of  oxidation
            as  compared  to 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, but the Eh of  deep-sea sediments may range from -150  to -100  mV.
              The  aerobic  bacteria  die  when  the free oxygen is totally  consumed; the
            anaerobic bacteria attack the sulfate ion, which is the second most important
            anion in the sea water. During this attack, the sulfate reduces to sulfite and
            then  to sulfide; the  Eh  drops to -600  mV;  H2S is  liberated,  and CaC03
            precipitates as the pH rises above 8.5 (Dapples, 1959).




              The  term  pH  means  the  logarithm  (base  10) of  the reciprocal  of  the
           hydrogen-ion concentration, and the pH  of pure water at 25OC is 7.0, which
           means  that  there  is  lo-’   ‘mole  per  liter  of  H+ in  solution.  When  other
           constituents  are  solubilized by  water, the pH  probably  will change because
           the chemical  equilibrium shifts as new ions combine with H+ or OH-.  The
           presence  of  slightly  dissociated  acids  or  bases will tend to buffer  the solu-
           tion, and the addition of  H+ or OH-  will shift the pH  only a small amount
           until the acids or bases are changed to salts.
              The  pH  of  oilfield  waters  usually  is  controlled  by  the carbon dioxide-
           bicarbonate  system.  Because  the  solubility  of  carbon  dioxide  is  directly
           proportional  to temperature  and  pressure,  the  pH  measurement should be
           made in the field if  a close-to-natural-conditions value is desired. The pH of
           the water is not used for water identification or correlation purposes, but it
           will  indicate  possible scale-forming or corrosion tendencies of  a water. The
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