ACS Catalysis
Research Article
(
catalytically active) material on the electrode, strongly
(OTf) ], the onset potential was found at about 1.7 V versus
2
suggesting that the catalytic water oxidation takes place in
the homogeneous phase.
In terms of molecular nature and catalytic current, the
performance of the Fe(mcp) systems is similar to that of the
dinuclear iron catalyst [(MeOH)Fe(Hbbpya)−μ−O−
RHE under electrochemical conditions (pH 5). This value
correlates well with the previously calculated redox potentials
V
IV
of the Fe /Fe redox couple for the α-[Fe(mep)(OTf)2]
complex (mep = N,N′-dimethyl-N,N′-bis(2-pyridylmethyl)-
ethylenediamine). A redox potential value of 1.73 V versus
33
IV
V
(
Hbbpya)Fe(MeOH)](OTf) . Moreover, both complexes
NHE was found for the Fe (O)(OH ) to Fe (O)(OH)
2
73
4
showed an overpotential in the range of 300−500 mV with
respect to the thermodynamic water oxidation potential of 1.23
V. In terms of TOF the Fe(mcp) systems showed a value of
transition (computed at pH 1). In addition, previous studies
IV
determined that Fe (O)(OH ) species in related nonheme
2
complexes were not able to form the O−O bond required for
−
1
25,37,38
74
0
.41 s in the presence of chemical oxidants
and the
oxygen evolution. Therefore, it is reasonable to suggest that
−
1
Fe(Hbbpya) system showed a value of 0.12 s under
the onset of the electrocatalytic wave may correspond to the
33
V
IV
electrochemical conditions. . The advantage of the Fe(mcp)
system is that it was proved to be active under both neutral and
acidic pH conditions, providing that one starts with a +III
precursor, whereas [(MeOH)Fe(Hbbpya)−μ−O−(Hbbpya)-
Fe(MeOH)](OTf) did not show stability at pH 1. It should
be mentioned though that α-[Fe(mcp)(OTf) ] showed good
catalytic rates at low pH in the presence of cerium(IV)
ammonium nitrate (CAN), but the electrochemical studies of
α-[Fe(mcp)(OTf) ] under such low pH conditions were
formation of Fe (O)(OH) from Fe (O)(OH ) species, and is
2
the rds.
When comparing the catalytic mechanism between electro-
chemical conditions and chemical oxidant-driven conditions
for Fe(mcp) and related complexes, clear differences between
the two regimes become apparent. These differences are most
notable when comparing the KIE values obtained under
electrocatalytic conditions to KIE values obtained when water
oxidation is driven by chemical oxidants. The [Fe-
4
2
2
excluded because of the demetallation of the iron(II)
precursor, which occurs on the time scale required for the
electrochemical experiment. In the presence of CAN, the
iron(II) precursor is instantaneously oxidized to the iron(III)
species, which is stable against hydrolysis. Following a rational
(OTf) (pytacn)] (pytacn = 1-(2-pyridylmethyl)-4,7-dimethyl-
1,4,7-triazacyclononane) catalyst has been shown to perform
2
WO with a KIE of approximately 1 when using NaIO and
4
CAN, compared to a KIE of 10 under electrocatalytic
25
conditions. In order to determine whether these differences
in KIE arise from the different nature of the catalyst or by the
type of terminal oxidant (electrocatalysis vs chemical
oxidants), we have evaluated the KIE for the α-[Fe(mcp)-
design, the iron(III) complex α-[Fe(mcp)(Cl) ]Cl was proved
2
to be stable and active in the acidic electrolyte (pH 1, 0.1 M
H SO ). The TOF values found with our catalysts are still low
2
4
when compared to the pentanuclear iron catalyst reported by
Masaoka et al., with a TOF = 1900 s . However, the
pentanuclear system operated at an overpotential higher than
(OTf) ] complex when using chemical oxidants. Turnover
2
−1
32
which operates at low pH (pH = 0.8), we have found that the
KIE is ca. 1.0, which matches well with the electrochemistry
experiments under acidic conditions. Considering that a KIE of
10 was obtained electrochemically at higher pH values, we
5
00 mV and in an acetonitrile/water mixture. Therefore, our
Fe(mcp) water oxidation catalysts offer the advantages of
stability and activity at neutral and acidic pH values, a lower
overpotential compared to some of the benchmark systems,
2
6
31
33
including Fe(dpaq), Fe(cyclam), Fe(bbpya), and other
29
tetradentate polypyridyl type ligands, and the ability to
operate in aqueous solutions (dpaq = 2-[bis(pyridine-2-
ylmethyl)]amino-N-quinolin-8-yl-acetamido and bbpya =
N,N-bis(2,2′-bipyrid-6-yl)amine).
4.6 to 10, using NaIO as the oxidant (see Table S1). Again,
4
under these conditions, a KIE of approximately 1 is observed.
Therefore, chemical and electrochemical water oxidation
conducted at neutral pH values exhibits different KIE values
indicating that they have different rds.
However, in contrast to the results obtained for the iron
catalysts reported in this study, the manganese catalyst α-
Previous studies have addressed the mechanism of water
oxidation performed with the catalysts studied in this work in
[
Mn(mcp)(OTf) ] exhibits signs of complex degradation and
2
37,41,73
deposition of manganese oxide on the electrode, which is
responsible for the observed catalytic activity.
the presence of chemical oxidants.
In the particular case
of α-[Fe(mcp)(OTf) ], mechanistic studies under acidic
2
IV
Overall, the reaction rates for electrocatalytic water
oxidation in the presence of the Fe(mcp) systems are modest,
with an overpotential on the scale of approximately 500 mV
with respect to the thermodynamic potential of the water
oxidation reaction of 1.23 V, suggesting the existence of kinetic
barriers for the reaction. In this regard, previous work has
conditions using Ce as a sacrificial oxidant, aided by
spectroscopic analysis, have identified the high-valent inter-
IV
mediate Fe (O)(OH ) as the resting state at a low
2
IV
concentration of Ce . This species undergoes a one electron
oxidation to form Fe (O)(OH) via an inner sphere electron
V
IV
transfer process that proceeds through a heterometallic Fe −
III
IV
IV
shown that Fe /Fe oxidation on related complexes entails a
O−Ce species. The latter accumulates when large concen-
III
IV
IV
slow Fe (OH)/Fe (O) proton-coupled electron transfer
associated with relatively large reorganization energy values,
trations of Ce are used, enabling mass spectrometric and
37
IV
spectroscopic characterization. The heterometallic Fe −O−
Ce species constitutes the last detectable intermediate of the
72
IV
which presumably arise from a spin-state barrier.
Most notably, our mechanistic analyses indicate that the
electrocatalytic reaction is first order in the iron catalyst and
that the rds has a large KIE ∼ 10 at neutral pH.
In order to understand the origin of this large KIE, it should
be considered that under electrocatalytic conditions, the water
oxidation onset potential can be ascribed to the formation of
the catalytically active species. In the case of α-[Fe(mcp)-
catalytic cycle prior to dioxygen formation and its evolution
toward the reactive Fe (O)(OH) species via internal electron
V
transfer presumably constitutes the rds of the reaction.
Computational analysis indicates that attack of the water
V
molecule on Fe (O)(OH) is initially assisted by an interaction
73
with the hydroxide ligand at the same iron center. Proton-
coupled electron transfer from the incoming water molecule to
2
590
ACS Catal. 2021, 11, 2583−2595