Approximately 2.6 x 10(4) TBg (700,000 Ci) of I-131 were released to t
he air from reactor fuel processing plants on the Hanford Site in sout
hcentral Washington State from December 1944 through December 1949. Th
e Hanford Environmental Dose Reconstruction Project developed a suite
of codes to estimate the doses that might have resulted from these rel
eases. The Regional Atmospheric Transport Code for Hanford Emission Tr
acking (RATCHET) computer code is part of this suite. The RATCHET code
implements a Lagrangian-trajectory, Gaussian-puff dispersion model th
at uses hourly meteorological and release rate data to estimate daily
time-integrated air concentrations and surface contamination for use i
n dose estimates. In this model, iodine is treated as a mixture of thr
ee species (inorganic gases, organic gases, and particles). Model depo
sition parameters are functions of the mixture and meteorological cond
itions. A resistance model is used to calculate dry deposition velocit
ies. Equilibrium between concentrations in the precipitation and the a
ir near the ground is assumed in calculating wet deposition of gases,
and irreversible washout of the particles is assumed. RATCHET explicit
ly treats the uncertainties in model parameters and meteorological con
ditions. Uncertainties in I-131 release rates and partitioning among t
he nominal species are treated by varying model input. The results of
100 model runs for December 1944 through December 1949 indicate that m
onthly average air concentrations and deposition have uncertainties ra
nging from a factor of two near the center of the time-integrated plum
e to more than an order of magnitude near the edge. These results indi
cate that similar to 10% of the I-131 released to the atmosphere decay
ed during transit in the study area, similar to 56% was deposited with
in the study area, and the remaining 34% was transported out of the st
udy area while still in the air.