Page 120 - Geochemical Remote Sensing of The Sub-Surface
P. 120

Spontaneous potentials and electrochemical cells                      97

              The  principal  oxidising  agent  on  Earth  is  free  oxygen  (02(g)) ,  for  which  the  only
           significant  terrestrial  source  is  plant  photosynthesis.  The  only  appreciable  source  of
           oxygen  for  the  geological  subsurface  is  the  atmosphere,  which  contains  21%  oxygen.
           Since  redox  variability  in  shallow  Earth  materials  cannot  be  due  to  variations  in  the
           primary source  of oxidising  agents,  it must be due to:  (1) kinetic processes  that  limit the
           transfer of oxygen into the subsurface;  and/or (2) processes  that control  the  consumption
           of oxygen (i.e., that control the availability of reducing agents).
              The primary limitations on the transfer of oxygen into the subsurface  are its solubility
           in  water  and  its  slow  rate  of  aqueous  diffusion.  In  the  fully-saturated  groundwater
           environment  below  the water table,  the  concentration  of oxygen has  an upper  limit  from
           which  it can only decrease.  Its solubility  limits the concentration  to a maximum  of about
           10  ppm  at  25~   In  contrast,  the  maximum  concentration  of  gaseous  oxygen  in  the
           vadose  zone  is limited  only by its molar ratio  in the  atmosphere  and  can  therefore  reach
           210,000  ppm.  This  enormous  disparity  demonstrates  why  moisture  content  is  the  single
           most  important  factor controlling  the  availability of oxygen  in a geological  environment
           (it also  demonstrates  why  subaqueous  disposal  of sulphidic  mine  tailings  is  so  effective
           in  preventing  their  oxidation).  In  many  subsurface  environments,  the  water  table
           represents  a  sharp  redox  boundary  between  abundant  oxidising  agents  above  and
           abundant  reducing agents below.  This is particularly true in young exotic overburden.
              Most  of  the  other  surficial  factors  controlling  local  redox  conditions  involve
           processes  that  control  the  availability  of  reducing  agents.  Chief  amongst  these  is  the
           accumulation  of  organic  matter.  All  forms  of  organic  matter  are  reducing  relative  to
           oxygen  and  most  can  be  oxidised  fairly  quickly  in  Earth  materials  by  microorganisms.
           As  such,  the  oxidation  of organic  matter  is  one  of the  primary  consumers  of oxygen  in
           the  shallow  subsurface.  Typically,  higher  concentrations  of organic  matter  in  soils  lead
           to  more  reducing  conditions,  particularly  in  saturated  environments.  Also  important  is
           the  lability  (i.e.,  availability to  microorganisms  as  a  source  of metabolic  energy)  of the
           organic  matter.  Well-humified  peat  is  not  as  chemically  reducing  as  methanogenic
           organic  muck  in  a  perpetually  submerged  portion  of  a  bog  because  the  former  has
           already undergone  oxidation  of its most labile organic components.
              The  other  major  consumer  of oxygen  in  the  shallow  subsurface  is  the  oxidation  or
           weathering  of mineral  matter  and  particularly  of metallic  sulphides.  Areas  of unusually
           active  weathering,  due  either  to  large  accumulations  or  to  more  reactive  minerals,
           typically result  in  an  enhanced  consumption  of oxidising  agents  relative  to  surrounding
           areas  and  to  more  negative  redox  conditions.  The  dispersal  of the  dissolved  products  of
           weathering,  such as Fe z+, can affect redox conditions  at some distance  from the source.
              All  forms  of  mechanical  dispersion  of  rock  material  can  affect  the  availability  of
           reducing  agents.  Continental  glaciation  results  in the widespread  deposition  of relatively
           unoxidised  rock,  till,  clay  and  other  drift  materials  over  vast  areas.  Different  deposit
           types  (e.g.,  sand,  clay)  resulting  in  different  permeabilities  in  transported  materials  can
           also  lead to higher or lower water tables  and variable rates  of percolation  of oxygenated
           groundwater.  This  can  result  in  a poorer  availability  of oxidising  agents  in  fine-grained
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