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Carbon dioxide dispersion halos around mineral deposits               131

           surfaces of soil particles.  These two forms of CO2  (especially the former) therefore give
           a good indication at surface of buried and blind ore deposits.
              Some  contribution  to  these  patterns  may  come  from  CO2  released  by  post-
           mineralisation  fracturing  of fluid  inclusions  that  trapped  CO2  during  metallogenesis.  A
           third  source  is  the  release  of  CO2  from  carbonates  as  a  result  of  sulphide  oxidation.
           Where  mineralisation  is  deeply  buried  and  below  the  water  table,  however,  any
           contribution from this process seems likely to be small.



           Factors  affecting  carbon  dioxide  anomalies

              In  wet  soils,  background  levels  of  CO2  are  increased  due  to  the  hydrolysis  of
           carbonates.  A  traverse over mineralisation  at Zhanglian was sampled once when the  soil
           was  wet  and  again  in  early  spring  when  the  soil  was  relatively  drier.  Sampling  of wet
           soils  produces  a  number  of  false  anomalies  of  CO2,  whilst  the  dry  soils  produced  a
           satisfactory low contrast CO2 anomaly over the mineralisation  only.  Therefore  sampling
           along river banks  or  in  soils  of varying moisture  content  should  be  avoided  in  order  to
           obtain clear anomaly definition.
              Thin  soils  underlain  by  limestone  can  also  be  the  source  of  false  anomalies.  On  a
           traverse  across  a  molybdenum  deposit  at Tongshan,  Jiangsu  province,  which  is  covered
           by  0.3-1.0  m  of eluvium,  CO2  anomalies  were  found  not  only  above  the  ore  body  but
           also  on  a  nearby  ridge.  Here  soils  are  particularly  thin  and  poorly  developed,  and  the
           underlying  limestone  creates  an  environment  in  which  the  pH  can  be  as  high  as  8.5,
           allowing carbonate enrichment which in turn produces a false anomaly of CO2.
              The natural organic carbon content of the soil can affect the amount of CO2  detected,
           and evidence  from one  traverse  suggests that proximity to the  exhaust  residues  of  road
           traffic could also be a source of CO2  in soil. The ratio of CO2  to organic carbon can be
           used to resolve this problem.


           CONCLUSIONS


              Carbon  dioxide,  probably  introduced  at  the  time  of emplacement  of mineralisation,
           occurs in a form that is easily released at  100~  as halo around and above many mineral
           deposits.  Along soil traverses  over nine  mineral  deposits  in China,  determination  of this
           CO2  yields  good-contrast  anomalies,  even  when  the  mineralisation  is  deeply  buried.
           There is also an elevated CO2 expression in soils over faults in mineralised areas.
              In  general,  over  those  mineral  deposits  in  China  where  both  methods  have  been
           tested,  there  is considerable  agreement between  CO2 patterns  and thermally-released  Hg
           patterns  (Chapter  13). The  continuity and  intensity of CO2 anomalies  tends  to be  a  little
           poorer.  On the  other hand,  in some cases  CO2 anomalies are present  over mineralisation
           where thermally-released Hg anomalies are absent.
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