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118                  Radiochemistry  and Nuclear  Chemistry


               Effluents  may also come from  large radiotracer users  (especially hospitals).  In  most  cases
               these releases  are well known  and  the area concerned  ('contaminated')  identified.  From a
               global  standpoint,  compared  to natural  radioactivity,  these releases are minor,  but  they do
               add  to  the  our  "natural"  radiation  background,  as  discussed  in  Chapters  18  and  22.
                Usually  one  distinguishes  between  "near  field"  and  "far  field"  effects  of  radioactivity
               releases.  Near  field  effects  are  observed  close  to  the  release  source,  as  for  example  the
               nuclear  power  plant or nuclear  waste  storage facility.  The dissolution  of nuclear  waste by
               rain  or  ground  water  is  a  typical  near  field  problem.  As  the  source  is  known,  it  can  be
               controlled  and  its  environment  monitored.  If  the  radioactivity  exceeds  permitted  levels,
               access  to the contaminated  area can be restricted.  Far  field  effects involve  the behavior  of
               radionuclides  which  have  spread  out  of  such  a  restricted  area,  caused  either  by  nuclear
               power  accidents  and  weapons  tests  or by  leakage  from nuclear power  plants.
                In  this  paragraph  we briefly  describe  some of the  largest  anthropogenic  sources  causing
               far  field  effects,  i.e.  nuclear  weapons  tests  and  nuclear  power  plant  accidents.  The  cause
               of  the  releases  is  discussed  in  Chapter  19.  Chapter  22  discusses  both  near  and  far  field
               effects in further detail,  particulary with regard to chemical properties:  liquid releases from
               nuclear power plants,  dissolution of solidified nuclear waste and of fall-out particles,  migra-
               tion  in  the  environment,  and  possible  consequences.



               5.10.1.  Nuclear  weapons

                Nuclear weapons  were tested in the atmosphere up  to  1990,  with total releases up  to 2  x
               1020 Bq  fission  products,  as  well  as  some  lesser amounts  of Pu  isotopes;  cf.  Table  22.2.
               Most  of  the  debris  injected  into  the  troposphere  had  a  mean  residence  time  of  ~-30  d,
               causing  fall-out  mostly  in  the  neighborhood  of  the  test  area.  Some  of  the  debris  passed
               through  the tropopause  and entered  the stratosphere  where  it was carried  by  winds  around
               the globe at approximately the latitude of the release.  The residence time in the stratosphere



                        TABLE 5.4. Events leading to large injections of radionuclides into the atmosphere

                        Source         Country  Time   Radioactivity   Important
                                                         Bq        nuclides
                        Hiroshima      Japan   1945     4 x 1016   Fiss.prod.
                        & Nagasaki                                 Actinides

                        Atmospheric    USA    -  1963   2 x 102o   Fiss. prod.
                        weapons tests   USSR                       Actinides

                        Windscale      UK     1957      1  •  1015   1311
                        Chelyabinsk    USSR   1957      8 X 1016   Fiss. prod.
                        (Kysthym)                                  9OSr '  137Cs
                        Harrisburg     USA    1979      I x 1012   Noble gases, 131I
                        Chernobyl      USSR   1986      2 x 1018   137Cs
   127   128   129   130   131   132   133   134   135   136   137