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Light hydrocarbons for petroleum and gas prospecting                  159

           detector  which  yields  a  total  hydrocarbon  signal.  This  system  is  claimed  to  produce
           direct vertical anomalies over reservoirs at depth. This technology appears reasonable  for
           detection  of seepage  which  is  large  enough  to  produce  free  gas  bubbles,  but  for  feeble
           seepage  (i.e.,  below water  solubility levels)  the  effectiveness  would seem to be  reduced
           by dispersion due to underwater currents.



           Soil gas

              The  hydrocarbon  gases  migrating  through  soil  pore  spaces  are  not  dissipated  and
           diluted  to  the  same  extent  as  those  in  the  atmosphere.  There  are,  however,  problems
           posed  by  the  very  low  levels  of hydrocarbon  gases  and  by  the  diurnal  "breathing"  of
           many near-surface  soils. In order to overcome these problems,  soil-gas techniques  which
           integrate  the  hydrocarbon  signal  were  introduced  by  Pirson  (1946),  Horvitz  (1950),
           Kartsev et al. (1959),  Karim (1964), Heemstra et al.  (1979), Hickey (1983), Hickey et al.
           (1983) and Klusman and Voorhees (1983).
              Karim (1964)  published  data on laboratory adsorption studies  for light hydrocarbons
           using activated  charcoal,  molecular sieve  (diatomaceous  earth)  and  silica gel.  As  shown
           in Table  5-VII, these substrates greatly increase the concentrations  available  for analysis,
           but  selective  adsorption  severely  affects  the  relative  compositions  of  the  individual
           gases.  The  lightest  gases  are  obviously  not  as  effectively  trapped  by  adsorption
           techniques  as  are  the  heavier,  less  volatile  components.  This  is  particularly  true  for
           methane and ethane.  The adsorption capacities of the substrates are also strongly reduced
           by moisture  content,  which  may vary from site to site, particularly  since  the  sampling  is
           conducted  in  the  ground  where  moisture  content  varies  more  rapidly  than  in  the
           atmosphere.
              Klusman  and  Voorhees  (1983)  introduced  a  variation  of this  technique  which  uses
           sample  collection on charcoal  wire  over extended  collection times,  followed by analysis
           using  a  quadrupole  mass  spectrometer.  The  advantages  cited  are  lower  field  expenses,
           increased  field  mobility,  improved  signal-to-noise  ratio  and  negation  of barometric  and
           other  meteorological  factors.  Major  drawbacks  are  that  the  most  mobile  light gases  are
           not collected by the charcoal  wire,  so that the  samples comprise  mainly the  intermediate
           to  heavier  molecular-weight  components,  which  include  butane  through  gasoline  and
           diesel.  Multivariate  statistical  techniques  are  required  to  interpret  the  large  number  of
           mass peaks  recorded,  which  includes  both parent  and multiple  daughters.  In  some  cases
           qualitative  information  based  on  fragment  patterns  of  the  adsorbed  compounds  is
           possible  (Fig.  5-17).  However,  different  molecular  species  and  their  fragment  patterns
           overlap;  for  example,  propane  and  carbon  dioxide  have  identical  masses  (44)  and  thus
           cannot  be  separated.  The  exploration  value  of  these  data  lies  in  the  demonstrated
           presence  of reservoir-type  hydrocarbons  at the  surface  and the  composition noted  in the
           lighter to heavier fragment patterns.
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