showed that at atmospheric pressure and room temperature,
SO2 adsorbed onto NC-Al2O3 up to 3.5
molecules of SO2/nm2, similarly on CM-Al2O3 there
were 3.5 molecules of SO2/nm2 adsorbed, and on NC(1/1)Al2O3/MgO there were 6.8 molecules of SO2/nm2,
whereas on CM-MgO there were only 0.68 molecules
of SO2/nm2 adsorbed (Table 5). These data indicate that
NC-Al2O3/MgO efficiently adsorb SO2 in slightly more
than one layer. After adsorption had ceased, the samples
were subjected to dynamic vacuum for 100 min to
remove the physisorbed species. After this vacuum
treatment, there remained 1.70 and 0.45 molecules of
SO2/nm2 present chemisorbed onto the NC-Al2O3, and
CM-Al2O3 samples, respectively. The vacuum treatment
removed most of the adsorbed SO2 from the CMMgO,
whereas the NC-Al2O3/MgO sample retained 3.9
molecules of SO2/nm2.
Next, an in situ IR study was performed to help
identify how the SO2 was binding.41 This setup allows
IR spectra to be obtained of the exact same spot before
SO2, with SO2, and after evacuation of SO2. The study
was conducted at room temperature with 20 Torr of SO2.
(40) Barin, I.; Knacke, O. Thermochemical Properties of Inorganic
Substances; Springer-Verlag: Berlin, 1973.
Table 4. Reaction of Pulses of CCl4 with Oxide Samples at 500 °C
sample breakthrough saturation molar ratio
NC-Al2O3 57 98 1.44 mol of CCl4:1 mol of Al2O3
CM-Al2O3 2 17 1 mol of CCl4:16 mol of Al2O3
NC-(1/1)Al2O3/MgO 25 88 1.8 mol of CCl4:1 mol of Al2O3/MgO
CM-MgO 1 4 1 mol of CCl4:32 mol of MgO
a Theoretical molar ratio: 1 mol of CCl4:2 mol of MgO, 1.5 mol of CCl4:1 mol of Al2O3, 2 mol of CCl4:1 mol of Al2O3/MgO. b NC-MgO
studied at 400 °C.51
Figure 4. X-ray diffraction patterns for CM-Al2O3, CMMgO,
NC-MgO, NC-Al2O3, and NC-(1/1)Al2O3/MgO.
Table 5. Adsorption of SO2 on Al2O3, MgO, and
Al2O3/MgO Samples at Room Temperature
sample
tot. molecules
of SO2/nm2
adsorbed
molecules of
SO2/nm2
physisorbed
molecules of
SO2/nm2
chemisorbed
NC-Al2O3 3.5 1.8 1.7
CM-Al2O3 3.5 3.0 0.45
NC-Al2O3/MgO 6.8 2.9 3.9
CM-MgO 0.68 0.51 0.17
NC-MgO35 6.0 1.5 4.5
2 Al2O3 + 3CCl4 f 3CO2+ 2Al2Cl6
2 MgO + CCl4 f CO2+ 2MgCl2
F Chem. Mater. Carnes et al.
Figure 6 shows the spectra after a 2 h evacuation for
all four samples. Both CM-MgO, and CM-Al2O3 showed
no adsorbed species. Both NC-Al2O3 and NC-Al2O3/
MgO show new peaks at 1135 and 1330 cm-1 that
correspond to chemisorbed monodentate SO2 adsorbed
species.35,42-46 These results indicate that the NC
samples have a high capacity for chemisorption of SO2
(Table 5) per unit surface area, indicating an intrinsically
higher activity.
Destructive Adsorption of Diethyl 4-Nitrophenyl
Phosphate (Paraoxon). The adsorption of Paraoxon
was carried out to compare the rates and capacities for
the metal oxide samples to dissociatively chemisorb a
polar organic, more specifically a toxic insecticide. By
monitoring of the disappearance of an UV band for
Paraoxon in pentane, the data shown in Table 6 were
obtained, and the results are striking. Neither of the
CM samples adsorbed much Paraoxon, while the NC
samples rapidly adsorbed the entire sample and developed
a bright yellow color, indicating the likely formation
of the p-nitrophenoxide anion on the surface.
Additional experiments with larger and larger amounts
of Paraoxon were studied, and it was found that about
5.5 ÌL of Paraoxon (2.55 _ 10-5 mol, 1.54 _ 1019
molecules) was adsorbed by 0.0300 g of NC-Al2O3, and
about 9.5 ÌL of liquid Paraoxon (4.40 _ 10-5 mol, 2.65
_ 1019 molecules) was taken up by 0.0350 g of NCAl2O3/
MgO. One molecule of Paraoxon dissociated and
with the p-nitrophenoxide lying flat would occupy about
1 nm2 of surface area. In a 0.0300 g sample of NCAl2O3
2.4 _ 1019 nm2 surface area is available, and so
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