cles.[11] Furthermore, by using sodium dioctyl sulfosuccinate
(AOT)–water–oil reverse micellar systems, copper nanopar-
ticles, nanorods, and nanodisks, the sizes and shapes of
which were controlled by regulating the water content in the
oil phase and/or the concentration of reducing agent or salt,
were synthesized.[12–15] Other capping agents such as cetyltri-
methylammonium bromide (CTAB),[16] sodium dodecylben-
zene sulfonate (DBS),[17] ethylenediamine (EDA),[18] and
poly(vinylpyrolidone) (PVP)[19] were also successfully used
to synthesize copper nanoparticles with shapes including
spheres, cubes, and wires, from the reduction of Cu(OH)2
with hydrazine in the presence of these surfactants. The
second synthetic approach to generate copper nanoparticles
is performed in high-boiling-point organic solvents by de-
composing various types of copper complexes at an elevated
reaction temperature in the presence of capping agents. For
instance, copper nanoparticles with different shapes such as
rods and cubes were synthesized by decomposing [Cu-
faceted crystalline copper nanoparticles showed high catalyt-
ꢀ
ic activity towards N-arylation of heterocycles by C N cou-
pling between aryl halides and N-heterocycles under mild
and aerated reaction conditions. Furthermore, the Cu nano-
particles effectively catalyzed the Mannich coupling reaction
of three reactants (para-substituted benzaldehyde, aniline,
and acetophenone) in one pot.
Results and Discussion
Synthesis of copper nanoparticles by optimizing the pH of
the solution (effect of pH): Although the chemistry and
most of the procedures we used to make copper nanoparti-
cles and the ones previously reported for making copper(I)
oxide nanowires[30] are similar, the two syntheses resulted in
completely different types of nanomaterials. In the synthesis
of copper(I) oxide nanowires, the primary reaction involves
the reduction of copper(II) salts with hydrazine in PVP pro-
ducing yellowish-colored samples of Cu2O nanowires. Here
in our case, the key modification of using PAA as capping
agent resulted in faceted crystalline copper nanoparticles in-
stead of copper(I) oxide, although the same reduction step
was employed. In aqueous solution, the chains of the PAA
polymer extend from the copper nanoparticle surface and
provide the nanoparticles steric stabilization from aggrega-
tion. It is also worth mentioning that the synthetic route
with PVP capping agent[30] does not produce pure copper
nanoparticles even in a wide pH range. Although our syn-
thetic method is somewhat similar to the one described in
reference [30], the use of PAA as a capping agent made the
pH optimum enough to favor the formation of pure copper
rather than copper oxide. An additional advantage of the
PAA capping agent is the extension of its uncoordinated
carboxylate groups into aqueous solution conferring the par-
ticles a high degree of dispersion in water.
Figure 1 shows typical UV/Vis absorption spectra of
PAA-capped copper nanoparticles that were synthesized at
various pH values and a graph of their absorption maxima
versus the pH. The UV/Vis absorption spectra of the as-pre-
pared copper nanoparticles display a well-defined absorp-
tion peak at around l=565 nm (Figure 1A). The absorption
peak can be attributed to the excitation of plasmon reso-
nance or interband transition, which is a characteristic prop-
erty of the metallic nature of copper nanoparticles.[31] The
appearance of this absorption peak further indicates the re-
duction of copper ions into copper nanoparticles under our
synthetic conditions.
ACHTUNGTRENNUNG(acac)2] (acac=acetylacetonate) in octyl ether with oleic
acid or oleyl amine capping agent at different reaction tem-
peratures.[20] The formation of the shaped nanoparticles was
attributed to three sequential events: initial nucleation of
seed metal clusters, preferential adsorption of capping
agents on selected facets of the seed nanocrystal, and aniso-
tropic growth of the metal in the other facets. Similarly,
shaped Cu nanoplates with intense plasmon resonances
were also obtained in N,N-dimethylformamide (DMF) sol-
vent.[21] In the third synthetic approach, called the polyol re-
duction method, ethylene glycol serves as the solvent and
the reductant for copper ions with PVP capping agent to
produce copper nanomaterials.[22] The fourth reported
method involves bioinspired synthetic routes that use a histi-
dine-containing peptide backbone to synthesize and control
the size of copper nanomaterials.[23] The conformational
changes in the peptide backbone have been correlated to
the size and the degree of dispersity of the nanoparticles.[23]
Finally, physical vapor deposition,[24,25] chemical vapor depo-
sition,[26] g irradiation,[27] irradiation with UV light,[28] and
sonochemical methods[29] have been reported for the synthe-
sis of copper nanostructures. However, the development of
aqueous-phase synthetic methods to shaped copper nanopar-
ticles has been rarely explored because the propensity of
surface oxidation of copper makes it difficult to fabricate
chemically stable Cu colloids.
Herein, we report an aqueous-phase synthetic route to
pure faceted crystalline copper nanoparticles with tunable
size and shape. The synthesis involves the reduction of cop-
per(II) salts with hydrazine in presence of poly(acrylic acid)
(PAA) capping agent. By adding different amounts of PAA,
copper nanoparticles with tunable sizes and shapes were ob-
tained. For instance, the average size of the copper nanopar-
ticles was varied between 30 to 80 nm by simply changing
the concentration of PAA. Furthermore, the pH of the solu-
tion was determined to play a key role for the formation of
pure copper nanoparticles as opposed to copper oxide nano-
particles. By adjusting the amount of PAA, faceted crystal-
line copper nanoparticles were obtained. These as-prepared
Our studies indicated that setting the pH of the solution
to an appropriate value played an important role to obtain
pure copper nanomaterial as opposed to copper oxide nano-
material. Copper nanoparticles are only formed if the final
pH of the solution ranges between 9.2–10.5. From the UV/
Vis absorption spectra obtained at various pH values
(Figure 1), it was obvious that the intensity and position of
the absorption maxima changed at different pH values. At
lower pH (i.e., 9.2–10.3), the spectra exhibited an absorb-
10736
ꢀ 2010 Wiley-VCH Verlag GmbH & Co. KGaA, Weinheim
Chem. Eur. J. 2010, 16, 10735 – 10743