https://doi.org/10.1038/srep02916
“The importance of testing the impact of humidity lies in ascertaining the stability of the framework structure and retention of adsorption capacity after exposure to water in gas flows. Figure 4(a) depicts the relationship between adsorption capacity and relative humidity (RH). Results show that adsorption capacity increases slightly to 0.509 mmol/g at 10% RH, but decreases from 10% RH to 100% RH. The increased CO2 capacity may be attributed to electrostatic interactions between water bound to Cr3+ sites and the quadrupole moment of CO230. The slightly decreased CO2 capacity above 10% RH is due to the competitive adsorption of water and CO2. Unlike other MOFs such as HKUST-1 that lost about 25% of its adsorption capacity after exposure to a 30% RH gas flow or Mg2(dobdc) that experienced a 84% decrease in capacity, MIL-101(Cr) performed much better in humidified environments16,30.”
“Besides the gases H2O, CO2 and N2 that constitute 95% or more of typical flue gas, the more minor components like SO2 and NO can play a major role in affecting adsorption processes1. The effect of NO on adsorption capacity is shown in Figure 4(b). Capacity follows a gradually declining trend when the concentration of NO rises from 0 to 2000 ppm. The adsorption stability of MIL-101(Cr) in the presence of SO2 is illustrated in Figure 4(c). Results show that adsorption capacity changes very little when the concentration of SO2 rises from 0 to 2000 ppm. At SO2 concentrations of 0, 200, 500, 1000 and 2000 ppm, MIL-101(Cr) adsorption capacities are 0.495, 0.481, 0.486, 0.478 and 0.49 mmol/g.
The experimental results for the impact of SO2 and NO on MIL-101 are supported by the results of a simulation study. However, the influence of H2O determined here differs from the conclusion of that study, where the models predicted H2O would completely occupy the coordinatively unsaturated “open metal” sites17. A possible explanation for the relatively small effect of trace contaminants on CO2 adsorption may be as follows. Gas adsorption onto MIL-101(Cr) is a physical adsorption process; thus MIL-101(Cr) lacks the reactive functional groups to chemically adsorb the flue gas contaminants. Secondly, because concentrations of contaminants are always significantly less than that of CO2 in flue gas, trace gases that do adsorb onto the framework will be largely substituted by the much higher-concentrated CO2.”
“Figure 4 Effects of (a) moisture, (b) NO and (c) SO2 on 10 vol% CO2 adsorption on MIL-101(Cr) at 298 K.”