LIQUID-PHASE AEROBIC OXIDATION OF ALCOHOLS
251
2
. Contrary to the general assumption, oxidation of the 12. M u¨ ller, E., and Schwabe, K., Kolloid-Z. 52, 163 (1930).
1
1
3. DiCosimo, R., and Whitesides, G. M., J. Phys. Chem. 93, 768 (1989).
co-product hydrogen by oxygen is not a necessary require-
ment for achieving high reaction rates.
4. Mallat, T., Bodnar, Z., and Baiker, A., in “Catalytic Selective Oxida-
tion” (S. T. Oyama and J. W. Hightower, Eds.), Vol. 523, p. 308. Am.
Chem. Soc., Washington, DC, 1993.
3
. The major role of oxygen is the oxidation of strongly
adsorbed CO produced by decarbonylation-type side reac-
15. Mallat, T., and Baiker, A., Catal. Today 24, 143 (1995).
tions. Continuous oxidative removal of CO ensures a high 16. van Dam, H. E., and van Bekkum, H., React. Kinet. Catal. Lett. 40, 13
0
(
1989).
number of free Pd sites available for the dehydrogenation
reaction.
1
1
7. Schuurman, Y., Kuster, B. F. M., van der Wiele, K., and Marin, G. B.,
Appl. Catal. A 89, 47 (1992).
8. Mallat, T., Bodnar, Z., Maciejewski, M., and Baiker, A., Stud. Surf.
Sci. Catal. 82, 561 (1994).
4
. The Cn−1 hydrocarbon fragments (co-products of the
decarbonylation reactions), or the dimers and oligomers
formed from them on the metal surface, can also lead to 19. Br o¨ nnimann, C., Bodnar, Z., Hug, P., Mallat, T., and Baiker, A.,
J. Catal. 150, 199 (1994).
catalyst deactivation. Removal of these species by oxygen
is inefficient.
2
2
2
0. Markusse, A. P., Kuster, B. F. M., and Schouten, J. C., J. Mol. Catal. A
58, 215 (2000).
1
1. Nondek, L., Zdarova, D., Malek, J., and Chvalovsky, V., Collect. Czech.
Chem. Commun. 47, 1121 (1982).
2. Schuurman, Y., Kuster, B. F. M., van der Wiele, K., and Marin, G. B.,
Appl. Catal. A 89, 31 (1992).
We propose that this model can be applied to many other
alcohol oxidation reactions over platinum-group metal
catalysts. The large differences observed in the reactivity of
various metal catalysts may partly be due to the different 23. Markusse, A. P., Kuster, B. F. M., and Schouten, J. C., Stud. Surf. Sci.
Catal. 126, 273 (1999).
extent of catalyst poisoning by degradation products and
2
2
4. van Dam, H. E., Kieboom, A. P. G., and van Bekkum, H., Appl. Catal.
3, 361 (1987).
to the efficiency of oxygen to regenerate the active sites.
The contradictory observations concerning the role of oxy-
gen in the reaction mechanism may be explained by the
3
5. Dijkgraaf, P. J. M., Rijk, M. J. M., Meuldijk, J., and van der Wiele, K.,
J. Catal. 112, 329 (1988).
dramatic effect of oxidative removal of strongly adsorbed 26. Jelemensky, L., Kuster, B. F. M., and Marin, G. B., Catal. Lett. 30, 269
(
1995).
7. Jelemensky, L., Kuster, B. F. M., and Marin, G. B., Chem. Eng. Sci. 51,
767 (1996).
8. Mallat, T., Br o¨ nnimann, C., and Baiker, A., Appl. Catal. A 149, 103
1997).
degradation products on the reaction rate. A positive or-
der to oxygen in the kinetic analysis does not necessarily
indicate a Langmuir–Hinshelwood mechanism with direct
involvement of oxygen. An unambiguous interpretation of
2
2
1
(
the role of oxidizing species requires in situ investigation of 29. Mallat, T., Bodnar, Z., Hug, P., and Baiker, A., J. Catal. 153, 131 (1995).
the surface species and the role of the oxidation state of the 30. Ebitani, K., Fujie, Y., and Kaneda, K., Langmuir 15, 3557 (1999).
3
3
1. Borodzinski, A., and Bonarowska, M., Langmuir 13, 5613 (1997).
2. Harrick, N. J., “Internal Reflection Spectroscopy.” Interscience,
New York, 1967.
catalytic metal surface.
ACKNOWLEDGMENT
33. Ferri, D., B u¨ rgi, T., and Baiker, A., J. Phys. Chem. B 105, 3187 (2001).
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3
The authors thank Dr. Frank Krumeich for TEM measurements and
ETH-Zurich for financial support.
35. Davis, J. L., and Barteau, M. A., Surf. Sci. 187, 387 (1987).
36. Shekhar, R., Barteau, M. A., Plank, R. V., and Vohs, J. M., J. Phys.
Chem. B 101, 7939 (1997).
37. Eadon, G., and Sheikh, M. Y., J. Am. Chem. Soc. 96, 2288 (1974).
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