Page 14 - Geochemistry of Oil Field Waters
P. 14

INTRODUCTION                                                           3


            tions  proved  that  interstitial  water  was  generally  present  in  the  oil  sands.
            Publications by  Garrison (1935) and Schilthuis (1938) give detailed informa-
            tion  concerning the distribution of  water and oil in porous rocks, and of  the
            origin and occurrence of  “connate”  water with  information concerning the
            relationship of water saturation to formation permeability.
              The word  “connate”  was first used  by  Lane and Gordon (1908) to mean
            interstitial  water  that  was  deposited  with  the sediments.  The processes of
            rock  compaction  and  mineral  diagenesis  result  in  the  expulsion  of  large
            amounts of  water from sediments and movement out of the deposit through
            the  more  permeable  rocks.  It  is therefore  highly  unlikely  that  the  water
            now in any pore is the same as that which was there when the particles that
            surround it were deposited. White (1957) redefined connate water as “fossil”
            water; it has been out of  contact with the atmosphere for an appreciable part
            of  a geologic time period. Connate water is thus distinguished from meteoric
            water  which  has  entered  the  rocks  in  geologically recent  times,  and  from
            juvenile  water which has come from deep in the earth’s crust and has never
            been in contact with the atmosphere.
              Meanwhile  petroleum  engineers  and  geologists  had  learned  that  waters
            associated with petroleum could be identified with regard to the reservoir in
           which they occurred by  a knowledge of their chemical characteristics. Com-
            monly the waters from different strata differ considerably in their dissolved
           chemical constituents, making the identification of a water from a particular
            strata  easy.  However,  in  some  areas  the  concentrations  of  dissolved  con-
           stituents  in waters from different strata do not differ significantly, and the
           identification of such waters is difficult or impossible.
              The amount of  water  produced with the oil often increases as the amount
           of  oil produced decreases. If  this is edge water, nothing can be done about it.
           If  it  is  bottom  water,  the  well  can  be  plugged  back.  However,  it often is
           intrusive water  from a shallow sand gaining access to the well  from a leaky
           casing or faulty completion and this can be repaired.
              Enormous quantities  of  water  are  produced  with  the oil in some fields,
           and it is necessary to separate the oil from the water. Most of  the oil can be
           removed by settling. Often, however, an oil-in-water emulsion forms which is
           very  difficult  to break. In such cases, the oil is heated  and various surface-
           active chemicals are added to induce separation.
              In  the  early days, the water was dumped on the ground where it seeped
           below the land surface.  Until about  1930, the oilfield waters were disposed
           into local drainage, frequently killing fish and even surface vegetation. After
            1930, it became  common practice to evaporate the water in earthen pits or
           to inject  it into the producing  sand  or another deep aquifer. The primary
           concern in such disposal practice is to remove all oil and basic sediment from
           the waters before  pumping them into injection wells, to prevent clogging of
           the  pore  spaces in the formation receiving the waste water. Chemical com-
           patibility of waste water and host aquifer water must also be assured.
              Waters produced  with petroleum are growing in importance. In years past,
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