it being abundant, clean, and atom-efficient. Although
considerable progress has been made, most of the aerobic
CDC reactions are carried out in organic solvents. It seems
difficult to realize a CDC reaction in water that is safe and
environmentally benign. In 2006, Li and Wang reported an
efficient “on water”-promoted direct coupling of 1,4-ben-
zoquinones with indole compounds.6 Later, Li et al. found
that copper salts could catalyze the aerobic CDC reaction
of tertiary amines with nitroalkanes or dialkyl malon-
ates to proceed efficiently in water.7 Lipshutz et al. recently
employed cationic [Pd(MeCN)4](BF4)2 salts as a catalyst
to activate aromatic CÀH bonds for the FujiwaraÀ
Moritani reaction of anilides in water.8 Nonetheless, exam-
ples on aerobic CDC reactions in water6À9 that are as
stable and efficient as those in organic solvents are
quite rare.
In this contribution, we wish to report an aerobic CDC
reaction in water, in which graphene, a two-dimensional
sp2-hybridized carbon network, was incorporated into the
transition-metal-catalyzed CDC reaction. It is anticipated
that the excellent electronic, mechanical, and thermal
properties10 of graphene would be useful not only to
provide a support for the transition metal catalyst but also
to improve the performance of the CDC reaction. In order
to make the whole system water-soluble, sulfonic groups
were used to functionalize graphene in this work. Inspired
by the work of Murahashi,2a who discovered RuCl3-
catalyzed oxidation of tetrahydroisoquinolines by oxygen,
we expected that RuCl3 could be successfully anchored on
the surface of the water-soluble graphene with sulfonic
groups. However, we found that RuO2 nH2O rather than
3
RuCl3 was formed on the surface of the graphene in situ.
More importantly, graphene-supported RuO2 (G-RuO2)
isabletocatalyzethe CDC reactionbetween tertiary amine
and nitroalkane under an oxygen atmosphere in water.
A comparison of the performance revealed that G-RuO2
Scheme 1. Preparation of the Water-Soluble Nanocomposites
nanocomposites are more efficient than RuCl3 nH2O and
3
RuO2 nH2O under the same condition. Moreover, G-RuO2
catalyst could be recycled simply by filtration.
3
The synthetic route to the nanocomposites is shown in
Scheme 1. Graphite oxide was prepared by a modified
Hummers’ method from graphite powder11 and used as the
starting material. Under the reduction by NaBH4, the ma-
jority of the oxygen functional groups on the graphite oxide
was removed, and sulfonation of the preliminarily reduced
graphene by aryl diazonium salt of sulfanilic acid12 afforded
water-soluble graphene. After addition of RuCl3 nH2O into
3
the aqueous solution of the sulfonated graphene, sodium
citrate aqueous solution was further added dropwise to
reduce the graphene under heat for 10 h. Then centrifugation
was carried out to obtain the nanocomposite.
Transmission electron microscopy (TEM) equipped
with energy-dispersive spectroscopy (EDS) and X-ray
photoelectron spectroscopy (XPS) were used to study the
chemical nature of the catalyst. As shown in Figure 1a,b,
the reduced graphene oxide sheets are slightly wrinkled
and folded on the ultrathin carbon membrane. The nano-
particles were about 2 nm in size and well-dispersed on the
surface of the transparent carbon sheet. Almost no particle
was found to scatter out of the surface of graphene,
indicating the strong interaction between the graphene
and the particles. The EDS images confirmed the existence
of S and Ru elements in the nanocomposite (Figure 1c).
The nature of nanoparticles on the surface of graphene was
further investigated by XPS measurements. Note that the
binding energies of Ru 3p3/2 and 3p1/2 at 463.4 and 486.3 eV
(Figure 1d), respectively, are consistent with the character of
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