Page 136 - Origin and Prediction of Abnormal Formation Pressures
P. 136

SMECTITE-ILLITE TRANSFORMATIONS                                       1 13

            in  shales  may  reduce  the  montmorillonite  dehydration  rate  and  release  of  water.  The
            result  will  be  similar  to  that  from  a  low  geothermal  gradient,  i.e.,  reduction  in  the
            rate  of  hydromica  formation  with  depth.  Under  favorable  conditions,  the  hydromicas
            may  also  be  hydrated;  this  is  accompanied  by  a  release  of  heat  and  leads  to  their
            transformation  to  a  secondary  montmorillonite.  The  relative  magnitudes  of desorption
            of water and hydromica hydration may determine the rate of development of anomalous
            pressure.
               The sedimentation rate and sediment sources do not remain constant with time;  some
            zones  may  differ in  the  dehydration rate  because  of changes  in  the  sedimentation  rate
            or  type  of  sedimentary  material.  Transitions  from  a  zone  with  normal  pressures  and
            normal dehydration rate to an AHFP zone may indicate either diagenetic and catagenetic
            processes,  or  a  lag  in  the  development  of  diagenetic  and  catagenetic  processes.  The
            montmorillonite content may remain the same or even increase with depth, but this does
            not  necessarily  mean  that  the  process  of dehydration  of montmorillonite  to  hydromica
            is replaced by the hydromica hydration, although this is possible. Instead, it could mean
            that  dehydration  process  in  the  AHFP  zones  is  slow;  therefore,  these  zones  may  be
            characterized by higher montmorillonite contents than those in younger zones of normal
            shale pore pressure.



            EFFECT OF HYDROCHEMICAL FACTORS

               The  hydrochemical  environment  in  a  basin  of  sedimentation  has  a  significant
            influence  on  the  intensity  of  postsedimentary  transformation.  First  it  is  important,
            therefore, to ascertain the nature of the hydrochemical regime observed in the Cenozoic
            complex of the South Caspian Basin, namely: whether it is a consequence  of diagenetic
            and  catagenetic  processes  in  shales  and  the  transformation  of  clay  minerals,  or  it  is
            formed  predominantly  as  a  result  of  the  action  of  other  factors.  In  this  connection,
            the problem  presenting  the  greatest interest is the  origin of the  inverted hydrochemical
            profile  in  the  section  of  the  South  Caspian  Basin,  i.e.,  replacement  of  deep  calcium
            chloride  waters  by  little-mineralized  sodium  bicarbonate  waters.  Numerous  data  from
            laboratory  analyses  and  field  observations  indicate  a  decrease  in  the  mineralization
            of  pore  waters  in  sands  with  depth.  Replacement  of  calcium  chloride  water  by  alkali
            sodium  bicarbonate  water  is  characteristic  for  the  AHFP  zones  in  the  South  Caspian
            Basin  areas  (Buryakovsky,  1974).  Analogous  data  on  the  decrease  of formation  water
            salinity  with  increasing  pressure  have  also  been  noted  in  the  Gulf  of  Mexico  (Fertl,
             1976).
               According to Chilingar (1957) the relationship between the chemical composition of
            the  Apsheron  Peninsula  waters  and  the  stratigraphic  depth  is  subject  to  the  following
            rules.  (1) The mineralization of water decreases with stratigraphic depth (also see Rieke
            and Chilingarian,  1974, pp.  265-269;  Samedov and Buryakovsky,  1966). (2) CI-,  Ca 2+,
             and Mg 2+ ions decrease with depth.  (3) (Na + +  K +) and (HCO~- +  CO 2-  +  H. K-) ions
            gradually increase  with depth.  (4) The transition from hard to alkaline waters  occurs  at
            maximum  concentration,  not  exceeding  0.1  g-equ  per  100  g  of  water  (5-6.5~   As
             a  rule,  the  waters  are  hard  at  concentrations  above  0.1  g-equ.  (5)  The  HCO~- content
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