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The cleaved off carbon formed the highly volatile and polymer-
izable formaldehyde which at lower temperatures could be
found as polyacetal solid at the bottom of the reactor. FTIR
tests of this undissolvable material revealed a clean spectrum of
polyacetal (Fig. S3, ESI†).
3 4
eFe O NS magnetic properties were exploited to improve
the ease and efficiency of removing the catalyst from solution.
Discontinuing the stirring allows the NS in solution to settle
onto the magnetic stirring bar allowing for the separation of the
catalyst from the liquid mixture and its recycling. Throughout 4
consecutive runs, conversion remained high while selectivity
dropped off and plateaued. Interestingly, in comparable
Fig. 2 Conversions (clustered columns) and benzaldehyde selectivity systems usually both selectivity and activity dropped upon
9
–11
(
lines) as a function of temperatures with Fe
eFe NS (red, dashed) as catalysts. Reaction conditions: 0.5 mol%
catalyst, 4 bar O , 24 h, 1.8 M acetonitrile.
3 4
O NS (blue, solid) and
recycling (Fig. 3).
1
3 4
TEM imaging of the eFe O NS after
3 4
O
and 2 recycle runs revealed they undergo slow dislocation,
possibly explaining the loss of selectivity after recycling (Fig. S5,
2
ESI†). Also oleylamine may play an active role in selectivity
5
as shown by others. A recycling catalytic test was run with
afford eFe O NS through a process delineated by Sun (Fig. S1,
3
4
2
5,26
eFe O NS and additional oleylamine, showing that a part of the
ESI†).
This material has been used as a drug delivery
3 4
selectivity could be recovered (Table S7, ESI†). Addition
of oleylamine to Fe O NPs, however, could not afford the
vehicle. It featured TEM-visible pores (Fig. 1, right), which
may allow a styrene molecule to enter the interior of the
3
4
superior activity and selectivity obtained with hollow structures
presented herein (Table S7, ESI†).
3 4 3 4
catalyst. Fe O NS and eFe O NS were compared in optimized
conditions, at 4 bar, in acetonitrile and for a range of tempera-
tures from 80 to 100 1C (Table 1 and Tables S4 and S5, ESI†).
Fig. 2 pictures well the trend of decreased selectivity with
increased temperature and increased conversion. The etched
In sum, we showed that the porous nature of the hollow iron
oxide nanoparticles allowed for a change in catalytic properties,
allowing the previously difficult oxidation of styrene with
molecular oxygen. Further compelling evidence for the use of
hollow iron oxide nanoparticles as a catalyst is that the oxida-
tion process can be controlled to stop at the aldehyde, giving
benzaldehyde as the major product.
3 4
particles eFe O NSs have marginally better selectivity and
significantly better conversions (+10–20 point%) over the range
of temperatures. The optimal reaction set is obtained for 90 1C
where conversion of 90% are combined to a high selectivity of
We thank the Natural Science and Engineering Research
Council of Canada (NSERC) Discovery Grant program, the
Canada Foundation for Innovation (CFI), the Canada Research
Chairs (CRC), the Fonds de Recherche du Qu ´e bec – Nature et
Technologies (FRQNT) Equipe program, the Centre for Green
Chemistry and Catalysis (CGCC), NSERC-Collaborative Research
and Training Experience (CREATE) in Green Chemistry and
McGill University for their financial support.
7
3% for the desired aldehyde product (TON§ = 131.4). This
result is unprecedented in terms of selectivity and activity
combined for this reaction with O . Preliminary kinetic data
suggested that eFe O NS were able to sustain high selectivities
over time in a unique fashion (Fig. S4, ESI†). Importantly, these
results were obtained in absence of non-noble metal (for compar-
ison see Table S6, ESI†).
As the product has one fewer carbons than the starting
material, the fate of the missing carbon was investigated.
2
3
4
Notes and references
‡
Octane and dodecane were both used as internal standards to
calculate conversion and selectivity percentages via GC-FID.
TON = number of moles of aldehyde produced per mole of catalyst.
13
§
1
2
3
4
U. Krings and R. G. Berger, Appl. Microbiol. Biotechnol., 1998, 49, 1–8.
S. Hughes, in Eur. Chem. Market, 2010, vol. 44.
J. A. B. Satrio and L. K. Doraiswamy, Chem. Eng. J., 2001, 82, 43–56.
F. Br u¨ hne and E. Wright, Ullmann’s Encyclopedia of Industrial
Chemistry, Wiley-VCH Verlag GmbH & Co. KGaA, 2000, DOI:
1
0.1002/14356007.a03_463.
J. Lv, Y. Shen, L. Peng, X. Guo and W. Ding, Chem. Commun., 2010,
6, 5909–5911.
5
6
7
4
K. Schr ¨o der, B. Join, A. J. Amali, K. Junge, X. Ribas, M. Costas and
M. Beller, Angew. Chem., Int. Ed., 2011, 50, 1425–1429.
B. Feng, Z. S. Hou, X. R. Wang, Y. Hu, H. Li and Y. X. Qiao, Green
Chem., 2009, 11, 1446–1452.
Fig. 3 Conversions (clustered columns) and benzaldehyde selectivity
8
9
M. Haruta, Nature, 2005, 437, 1098–1099.
(
lines) as a function of the number of recycle runs with eFe
catalysts. Reaction conditions: 0.5 mol% eFe NS catalyst, 4 bar O
4 h, 90 1C, 1.8 M acetonitrile.
3 4
O NS as
M. Turner, V. B. Golovko, O. P. H. Vaughan, P. Abdulkin,
A. Berenguer-Murcia, M. S. Tikhov, B. F. G. Johnson and
R. M. Lambert, Nature, 2008, 454, 981–983.
3
O
4
2
,
2
1
2484 | Chem. Commun., 2014, 50, 12482--12485
This journal is ©The Royal Society of Chemistry 2014