Page 159 - Geochemistry of Oil Field Waters
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BARIUM                                                               147


            170 ppm;  and  secondary  gypsum,  up to 1,100 ppm  (Goldschmidt, 1958).
            Sea water contains about  8 mg/l of  strontium, but subsurface brines contain
            up to 3,500 mg/l. Fig. 5.11 is a plot of chloride versus strontium content for
            some  subsurface  brines taken from some Tertiary, Cretaceous, and Jurassic
            age sediments. Most of  these samples were enriched in strontium compared
            to the evaporite-associated  water, and it is possible that a mechanism similar
            to dolomitization could cause the enrichment. In comparison to calcium, the
            strontium  appears  to be  increasingly accumulated; for  example,  only  five
            samples  (from  Tertiary  sediments)  fell  within  the  normal  evaporite  curve.
            Fig.  5.12 is a similar plot  for some subsurface brines showing similar results
            taken from sediments of Mississippian and Pennsylvanian age.

            Barium

              Barium, like strontium,  is a minor element, comprising 0.04 wt.%, of the
            earth’s crust; it is more concentrated in igneous rocks and less concentrated
            in  sedimentary  rocks  (Fleischer,  1962). It,  like  the  other  alkaline  earth
            metals,  is  predominantly  lithophile.  Table  5.111  illustrates  some  of  the
            properties  of  barium;  its ionic  radius,  1.35 A,  permits  it to replace  potas-
            sium,  but usually not  calcium and even less commonly magnesium. Barium
            forms  more  of  its  own  minerals  than  does  strontium.  Barium  is readily
            absorbed  by  colloids,  like  potassium,  and  is therefore  retained  by  soils or
            precipitated  with hydrolysates; it is also concentrated in deep-sea manganese
            nodules (Hem, 1970).
              Barium  dissolves as  bicarbonate,  chroride,  or  sulfate during  weathering
            processes,  and  migrates  in  aqueous  solutions  as  these  compounds.  The
            solubility of  barium sulfate increases when hydrochloric acid or chlorides of
            the alkali or other alkaline earth metals are present  in solution. The proper-
            ties  of  barium  are  similar to those  of  strontium. Both precipitate through
            loss of  carbon dioxide from a bicarbonate-bearing solution, or as sulfates by
            the action  of  sulfuric acid, sulfides, or sulfates. Strontium, however, is less
            likely to be absorbed by clays than barium, because its ionic radius is smaller
            and its ionic potential is higher.
              Encrustation deposits taken from plugged pipes of waterflood systems for
            secondary recovery  of  oil, where  barium  is present, usually contain barium,
            calcium,  strontium,  iron,  and  traces  of  other  metals.  Barium  may  cause
            problems  in waterflood  systems by reacting with the chromate-type oxygen-
            corrosion inhibitors, forming water-insoluble barium chromate.
              The  amount  of  barium  found  in  sandstones,  shales,  and  carbonates  is
            about  180, 450, and 90 ppm,  respectively  (Goldschmidt, 1958). Sea water
            contains about 0.03 mg/l, and subsurface brines may contain more than 100
            mg/l;  however,  many  brines  contain  less than  10 mg/l.  Davis  and  Collins
            (1971) found that 59 mg/l of  barium  sulfate is soluble in a synthetic brine
            with  an  innic  strength  of  3.0487, containing sodium, calcium, magnesium,
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