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Spontaneous potentials and electrochemical cells                      95


           Sources of spontaneous potential

              All moist  Earth materials  contain  redox-active  species,  such  as  O2(aq), Fe 2+, HS,  OH-
           and  H +, which  impart  a bulk  redox  capacity,  or  Eh  if measured  against  the  H+-H2 half-
           cell,  to  the  soil  or  groundwater.  The  variable  chemical  composition  of  overburden,
           groundwater  and  rock therefore  results  in variable  redox  capacity which,  in turn,  results
           in spontaneous  potential  voltages  and currents between  different points  in the Earth.  The
           multitude  of potential processes  that affect the composition  of Earth materials and might
           thereby  affect  redox  processes  can  be  divided  into  primary  lithological  processes  and
           surficial processes.
              Primary  lithological  processes  are  defined  as  all  those  that  contribute  to  the  variable
           composition  of  rock.  They  result  in  specific  lithologies  and  mineral  accumulations  in
           various places  in the upper crust.  The mineral  assemblages  in these  materials  can  impart
           a redox potential  to the groundwater/rock  matrix with  which  they are  in contact  and  can
           result  in  a  characteristic  redox  signature  for  various  rock  types  and  mineral
           accumulations.  For example,  the presence  of large amounts  of gypsum  in carbonate  rock
           can  fix  the  equilibrium  Eh  of  the  groundwater/rock  environment  to  no  lower  than
           approximately  -275  mV,  which  is the  Eh  of the  SO42"-HS  - half-cell  (at pH  8 and  using
           certain other assumptions;  Garrels and Christ,  1965, p.  215).  In this environment,  species
           that can impart a lower Eh are unlikely to be present because  most of the reducing agents
           capable  of reducing  8042  to  HS-would  already  have  been  consumed.  However,  the  Eh
           can  be  greater  than  -275  mV  because  SO42- is  the  only  geologically-important  sulphur
           species  in  oxidised  environments  (Krauskopf,  1979),  where  its  redox  behaviour  is
           relatively  inert  (Bartlett  and  James,  1995),  and  therefore  it  adds  little  to  the  redox-
           buffering of oxidised systems.
              Processes  such as these can occur due to mineral  assemblages  or dissolved  species  in
           many  other  rock  types.  In  unweathered  pyritic  rocks,  Eh  is  typically  maintained  below
           the  sulphide  oxidation  half-cell.  Ferrous  olivines  and  clinopyroxenes  in ultramafic  rocks
           undergoing  weathering  can produce  very reducing  conditions  that approach  the  limits  of
           water  stability  (around  -400  mV  at  pH  11;  Barnes  et  al.,  1978).  The  presence  of
           dissolved  oxygen  in oxygenated  terrestrial waters  typically maintains  Eh  at a  fairly high
           empirically-observed  level of over 200  mV.  The empirical  limit  is used  because  there  is
           no  perfect  correlation  between  dissolved  oxygen  concentration  and  Eh,  probably  due  to
           the myriad biological  and  inorganic  processes  that  involve  oxygen.  There  is, however,  a
           general  relationship  between  the presence  of dissolved  oxygen and high  Eh to the  extent
           that most oxygenated terrestrial  waters  are  found  to have  an  Eh of between  200  and 400
           mV.  The  upper  limit  of geologically  observed  Eh  is  around  800  mV  and  the  theoretical
           electrical potential of oxygen is higher still at  1000 mV at pH 4.0 (Fig. 3-4).
              The  presence  of water  itself restricts  the  Eh  of  aqueous  systems  to  a  well-defined
           stability field.  Figure 3-4 shows  the theoretical  and empirical  stability  fields  for water in
           natural  environments.  As  shown  in  Table  3-I,  reducing  agents  that  are  more  reducing
           than  H2(g) rarely  exist  in  the  shallow  terrestrial  environment  because  their  oxidation  by
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