This work is part of our continuing efforts to address engineering issues related to the removal of tritiated water from off-gases produced in used nuclear fuel reprocessing facilities. In the current study, adsorption equilibrium of water on molecular sieve 3A beads was investigated. Adsorption isotherms for water on the UOP molecular sieve 3A were measured by a continuous-flow adsorption system at 298, 313, 333, and 353 K. Experimental data collected were analyzed by the Generalized Statistical Thermodynamic Adsorption (GSTA) isotherm model. The K + /Na + molar ratio of this particular type of molecular sieve 3A was ∼4:6. Our results showed that the GSTA isotherm model worked very well to describe the equilibrium behavior of water adsorption on molecular sieve 3A. The optimum number of parameters for the current experimental data was determined to be a set of four equilibrium parameters. This result suggests that the adsorbent crystals contain four energetically distinct adsorption sites. In addition, it was found that water adsorption on molecular sieve 3A follows a three-stage adsorption process. This three-stage adsorption process confirmed different water adsorption sites in molecular sieve crystals. The second adsorption stage is significantly affected by the K + /Na + molar ratio. In this stage, the equilibrium adsorption capacity at a given water vapor pressure increases as the K + /Na + molar ratio increases.
The
objective of the current work was to shorten the gap for fundamental
adsorption kinetic data required for the development of advanced adsorption
unit-operation models to be incorporated into an overall plant-level
model for spent nuclear fuel reprocessing. The kinetics of water-vapor
adsorption on molecular sieve 3A was investigated at 25–80
°C and water dew points from −69 to 17 °C. Water
uptake curves were fitted with three kinetic models including the
linear-driving-force model, the shrinking-core model, and the Langmuir
kinetic model. The results suggest that the water-vapor adsorption
on molecular sieve 3A under the investigated experimental conditions
was controlled by both external film resistance and internal macropore
resistance. The contribution of the external film resistance varied
from 25% to 50% of the total mass-transfer resistance depending on
the adsorption temperature. It was also found that the Langmuir kinetic
model fitted individual sets of kinetic data very well, but the Langmuir
adsorption constant obtained from curve fitting decreased with increasing
adsorption temperature and with increasing water vapor pressure. This
result indicates a significant surface heterogeneity of molecular
sieve 3A and also implicitly verifies that the Langmuir isotherm model
is unable to represent isotherms of water adsorption on molecular
sieve 3A.
Capture
of radioactive iodine is a significant consideration during
reprocessing of spent nuclear fuel and disposal of legacy wastes.
While silver-exchanged mordenite (AgZ) is widely regarded as a benchmark
material for assessing iodine adsorption performance, previous research
efforts have largely focused on bulk material properties rather than
the underpinning molecular interactions that achieve effective iodine
capture. As a result, the fundamental understanding necessary to identify
and mitigate deactivation pathways for the recycle of AgZ is not available.
We applied X-ray Absorption Fine Structure (XAFS) spectroscopy to
investigate AgZ following activation, adsorption of iodine, regeneration,
and recycle, observing no appreciable degradation in performance due
to the highly controlled conditions under which the AgZ was maintained.
Fits of the extended XAFS (EXAFS) data reveal complete formation of
Ag0 nanoparticles upon treatment with H2, and
confirm the formation of α-AgI within the mordenite channels
in addition to surface γ/β-AgI nanoparticles following
iodine exposure. Analysis of the nanoparticle size and fractional
composition of α-AgI to γ/β-AgI supports ripening
of surface nanoparticles as a function of recycle. This work provides
a foundation for future investigation of AgZ deactivation under conditions
relevant to spent nuclear fuel reprocessing.
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