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tion conditions, thus, the factors of reaction conditions and re-
actants for studying the reaction mechanism can be eliminat-
ed.
or Fe3O4@SiO2-Pd. This assertion is based on the following ob-
servations.
During the experiment, we removed the catalyst with
a magnet, and permitted the reaction to continue. The yield
stopped increasing immediately for the Fe3O4@SiO2-Pd@mCeO2
catalyst but not for the Fe3O4@h-Pd@mCeO2 or Fe3O4@SiO2-Pd
catalysts (see Figure 6b). If a trace amount of soluble leaching
Pd species was the active species, the catalytic yield would
have increased, even after the removal of catalyst. The hot-fil-
tration tests indicated that the catalysis is from the leached Pd
over Fe3O4@h-Pd@mCeO2 and over Fe3O4@SiO2-Pd, and unclear
In addition to prominent catalytic activity, isolation and recy-
clability of a catalyst are considerable requirements for any
practical catalytic reaction. In our systems, the catalysts were
readily recovered from their dispersion using an external
magnet. To test the recyclability of the catalyst, a benchmark
reaction was chosen as a comparison. As illustrated in Fig-
ure S7a, the Fe3O4@SiO2-Pd@mCeO2 catalyst could be recycled
by using selective magnetic separation up to ten times with-
out a notable decrease in yield. However, as revealed by Figur-
es S7b and c, the recycling test for Fe3O4@h-Pd@mCeO2 and
Fe3O4@SiO2-Pd indicated a decrease in catalytic efficacy after
the reaction was repeated five and three times, respectively.
Assessing the leaching of active Pd NPs into the reaction
mixture is another key factor in testing the stability of the Pd
catalyst. To verify the possibility of leaching, the three kinds of
catalyst were detected by inductively coupled plasma atomic
emission spectrometry (ICP-AES) after ten cycles, five cycles,
and three cycles. The results are listed in Table S5 in the Sup-
porting Information. The benchmark reaction shows a determi-
nable Pd loss for the Fe3O4@SiO2-Pd@mCeO2 catalyst. This
result might, to some extent, explain the slight yield decreases
following increased recycling. Figures S8a and S9b show the
SEM and TEM images of the Fe3O4@SiO2-Pd@mCeO2 catalyst
for the Suzuki reactions after ten runs of recycling. These
images indicate that the catalyst retained its spherical shape
after recycling. For Fe3O4@h-Pd@mCeO2 and Fe3O4@SiO2-Pd
catalysts, the leaching of Pd NPs is notable (Table S5). The SEM
image of the Fe3O4@SiO2-Pd catalyst (Figure S9a), compared
with the TEM image (Figure 2a), reveals that most of the Pd
NPs leached into the solvent. The SEM image (Figure S8b) and
TEM images (Figures S9c and d) of the Fe3O4@h-Pd@mCeO2
catalyst display that most of the outer CeO2 shell was dam-
aged, while only parts of the catalyst maintained a yolk–shell
structure. Prominently, the recyclability of the Fe3O4@SiO2-
Pd@mCeO2 catalyst was the best among the three. One could
easily ratiocinate that the hierarchical core–shell structures ef-
fectively hinder the aggregation and leaching of Pd NPs owing
to the robust protection provided by porous CeO2 shells. The
easy isolation and good reusability of the catalyst illustrate
that our catalysts have high separability and stability for study-
ing a reaction mechanism.
over Fe3O4@SiO2-Pd@mCeO2.
A positive hot-filtration test
means the occurrence of homogeneous catalysis, whereas
a negative hot-filtration test does not necessarily imply the
emergence of heterogeneous catalysis for a number of reasons
(e.g., fast deactivation or redeposition of soluble active spe-
cies). Consequently, the distinction between heterogeneous
and homogeneous catalytic activity cannot be declared solely
based on the results of our hot-filtration test.[63]
The inverse relationship between the active Pd concentra-
tion and the conversion rate is associated with the homogene-
ous mechanism.[64] The inverse relationship refers to the rela-
tionship between the active Pd concentration and turnover
number (TON) or turnover frequency (TOF). If the TON or TOF
increases with decreasing active Pd concentration, it means
that the homogeneous rather than heterogeneous catalysis
works for the Suzuki reaction.[65] To investigate this inverse rela-
tionship, we assessed the effect of Pd concentration on catalyt-
ic activity. Figure 6c–e depicts the reaction profiles of the cata-
lyst with a Pd concentration of 0.1, 0.5, 1, and 5 mmol%. The
TON and TOF for the different Pd concentrations are shown in
Table S6. It is also clear from Table S6 that the TOF increases
on going from 5 to 0.1 mmol% over Fe3O4@h-Pd@mCeO2 and
over Fe3O4@SiO2-Pd, and is inconspicuous over Fe3O4@SiO2-
Pd@mCeO2. This can be explained by the equilibrium between
the Pd present in the clusters, which formed from the soluble
leaching of Pd, and the Pd NPs involved in the catalytic
cycle.[66] At lower Pd concentrations, this equilibrium can shift
away from the inactive clusters, resulting in a higher percent-
age of active Pd catalyst. The Fe3O4@SiO2-Pd@mCeO2 catalyst
(Figure 6d) displayed an increased conversion rate when the
Pd concentration increased. Interestingly, the Fe3O4@h-
Pd@mCeO2 and Fe3O4@SiO2-Pd catalysts did not show the
same reactivity trend when varying the Pd concentration. As il-
lustrated in Figure 6c,e, both the reactions with a Pd concen-
tration of 1 mmol% were faster than those with higher Pd con-
centrations (5 mmol%). This deactivation of Pd catalyst, the so-
called “homeopathic” mechanism, happened as a result of the
soluble leaching Pd nucleating to form Pd clusters that contin-
ued to grow.[9] As the Pd concentration increased, greater
leaching occurred, and the quenching of the active Pd catalyst
in solution became more efficient.
Another important aspect of a catalyst is the nature of
active noble-metal species (homogeneous or heterogeneous)
in cross-coupling reactions. The literature differs as to whether
the Pd-catalyzed Suzuki–Miyaura reactions result from leaching
Pd NPs or the heterogeneous Pd NPs themselves. This has
been a topic of intense debate and is far from being rid of
controversy. Thus, we carried out a hot-filtration test, solid-
phase poisoning, and assessed Pd concentrations to validate
whether the Pd active sites were encapsulated by the CeO2
shell, or the homogeneous Pd species leached from the CeO2
shell during the reaction process were true catalysts. The re-
sults imply that Fe3O4@SiO2-Pd@mCeO2 completes the reaction
in a true heterogeneous manner, but not Fe3O4@h-Pd@mCeO2
The benchmark reaction was also conducted in the presence
of poly(4-vinylpyridine) (PVPy), which is a well-known solid
poison that restricts homogeneous Pd species in the liquid
phase through chelation.[14] A comparison of conversion clearly
illustrates that the catalytic efficacy of the Fe3O4@SiO2-
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