Green Chemistry
Paper
mixture was stirred for 45 min and the color of the methanol
solution disappeared. The solid materials were filtered and
Acknowledgements
washed with deionized water (10 ml) and methanol (10 ml). This work was financially supported by the National Natural
The washing operation was repeated for three times. The Sciences Foundation of China (no. 21101161, 21174148).
resulting solid was suspended in methanol and NaBH4
(5.5 mg) in water (2 ml) was added under stirring. The solid
materials turned light gray. After filtration and washing, the
solid materials were dried under vacuum for 3 h. The Rh load
Notes and references
was 1.0 wt%.
1 A. Haynes, Adv. Catal., 2010, 53, 1.
Before the catalyst test, the catalyst was loaded with HI
through direct suspension in a HI methanol solution. The
iodide amount was controlled by the concentration of HI in
solution. The resulted materials were washed with deionized
water until no iodide anion was detected in the eluent through
silver cation test. After being washed with methanol and
diethyl ether sequentially, the catalyst was dried under
vacuum.
2 W. Reppe, H. Friederich, N. von Kutepow and W. Morsch,
US 2729651 (to BASF), 1956; W. Reppe and H. Friederich,
US 2789137 (to BASF), 1957.
3 F. E. Paulik and J. F. Roth, Chem. Commun., 1968, 1578.
4 P. R. Ellis, J. M. Pearson, A. Haynes, H. Adams, N. A. Bailey
and P. M. Maitlis, Organometallics, 1994, 13, 3215;
T. R. Griffin, D. B. Cook, A. Haynes, J. M. Pearson, D. Monti
and G. E. Morris, J. Am. Chem. Soc, 1996, 118, 3029;
G. J. Sunley and D. J. Watson, Catal. Today, 2000, 58, 293;
T. Ghaffar, J. P. H. Charmant, G. J. Sunley, G. E. Morris,
A. Haynes and P. M. Maitlis, Inorg. Chem. Commun., 2000,
3, 11; M. Cheong, R. Schmid and T. Ziegler, Organo-
metallics, 2000, 19, 1973.
5 T. W. Dekleva and D. Forster, Adv. Catal., 1986, 34, 81;
M. J. Howard, M. D. Jones, M. S. Roberts and S. A. Taylor,
Catal. Today, 1993, 18, 325; N. Yoneda, S. Kusano,
M. Yasui, P. Pujado and S. Wilcher, Appl. Catal., A, 2001,
221, 253; P. Torrence, in Applied Homogeneous Catalysis
with Organometallic Compounds, ed. B. Cornils and
W. A. Herrmann, Wiley-VCH, Weinheim, 2nd edn, 2002,
vol. 1, p. 104; C. M. Thomas and G. Süss-Fink, Coord.
Chem. Rev., 2003, 243, 125; P. Maitlis and A. Haynes, in
Metal-Catalysis in Industrial Organic Processes, ed. P. Maitis
and G. P. Chiusoli, Royal Society of Chemistry, Cambridge,
2006, p. 114; A. Haynes, Top. Organomet. Chem., 2006, 18,
179.
6 N. De Blasio, E. Tempesti, A. Kaddouri, C. Mazzocchia and
D. J. Cole-Hamilton, J. Catal., 1998, 176, 253; R. S. Drago,
E. D. Nyberg, A. El A’mma and A. Zombeck, Inorg. Chem.,
1981, 3, 641.
7 T. Minami, K. Shimokawa, K. Hamato, Y. Shiroto and
N. Yoneda, US Pat., 5364963 (to Chiyoda), 1994; Y. Shiroto,
K. Hamato, S. Asaoka and T. Maejima, European Patent,
0567331 (to Chiyoda), 1993; N. Yoneda, T. Minami,
J. Weiszmann and B. Spehlmann, Stud. Surf. Sci. Catal.,
1999, 121, 93.
Characterization methods
X-ray photoelectron spectroscopy (XPS) was performed over a
VG ESCA-Lab200I-XL instrument. All peak positions in XPS
experiments were calibrated by the binding energy of C 1s as
reference of 284.6 eV. An Eclipse V2.1 data analysis software
supplied by the VG ESCA-Lab200I-XL instrument manufacturer
was applied for the manipulation of the acquired spectra.
Transmission electron microscopy (TEM) was performed on a
JEOL 2010 TEM with an accelerating voltage of 200 kV. Elec-
tron Probe Microanalysis (EPMA) (carried out on EPMA1600,
SHIMADZU) was used to characterize the dispersion state of
rhodium nanoparticles. The rhodium concentrations in the
reaction mixture were determined by ICP-OES using a Perkin
Elmer Optima instrument. The ionic iodide content in the
reaction mixture was determined by a 797 VA Computrace
polarograph manufactured by Metrohm, the detection limit of
which was 0.1 ppb. Trace methyl iodide (CH3I) in the reaction
mixture was measured by a chromatograph with an ECD detec-
tor and backflushing technique. Nitrogen-adsorption isother-
mal and textural properties of the as-synthesized materials
were determined by using liquid nitrogen over a Quanta-
chrome Autosorb Automated Gas Sorption System (Quanta-
chrome Corporation).
The products were analyzed by GC and GC-MS. GC was
carried out over GC-2014 (SHIMADZU) with a high temperature
capillary column (MXT-1, 30 m, 0.25 mm ID) and a FID detec-
tor. GC-MS was carried out over GCT Premier/Waters with
capillary column (DB-5MS/J&W Scientific, 30 m, 0.25 mm ID).
8 H. Jiang, Z. Liu, P. Pan and G. Yuan, J. Mol. Catal. A: Chem.,
1999, 148, 215; F. Li, J. Huang, J. Zou, P. Pan and G. Yuan,
Appl. Catal., A, 2003, 251, 295; S. Zhang, C. Guo, Q. Qian
and G. Yuan, Catal. Commun., 2008, 853; F. Li, Q. Qian,
F. Yan and G. Yuan, Mater. Chem. Phys., 2008, 107, 310;
F. Li, J. Zou and G. Yuan, Catal. Lett., 2003, 89, 115.
9 The European Technology Platform for Sustainable Chem-
Test of the catalytic activity for methanol carbonylation
The catalyst tests were carried out in a 50 ml Hastelloy auto-
clave. Typical reaction conditions: the catalyst; 0.2 g, methanol;
10 ml, reaction temperature; 120 °C, CO pressure; 3.0 MPa,
reaction time; 180 min. Product–catalyst separation was
carried out through simple filtration in the five-run recyclabi-
lity test. In consecutive batch tests, a continuous filter was 10 C. Gabriele and P. Siglinda,in Sustainable Industrial
applied to separate the catalyst. The catalyst was recycled into
the autoclave with the methanol feedstock stream.
Processes, ed. C. Fabrizio, C. Gabriele, P. Siglinda and
T. Ferruccio, Wiley-VCH, Weinheim, 2009, pp. 1–72.
This journal is © The Royal Society of Chemistry 2013
Green Chem.