Simrjit Singh1,2, Mohd Faraz1, Neeraj Khare1. 1. Department of Physics, Indian Institute of Technology Delhi, New Delhi 110016, India. 2. Department of Electrical and Systems Engineering, University of Pennsylvania, Philadelphia, Pennsylvania 19104, United States.
Abstract
Semiconductor heterostructures have attracted intensive research attention during the past few years owing to their great potential for energy and environmental remediation related applications. Effective optical absorption and efficient separation of photogenerated charge carriers are among the key factors for achieving high efficiency in a photocatalytic process. This mini-review summarizes state-of-the-art activities in designing nanosemiconductor heterostructures using multifunctional semiconductors for solar-to-hydrogen conversion and degradation of organic pollutants. Various novel design strategies such as semiconductor/graphene heterojunctions including graphene as a semimetal and photosensitizer, semiconductor/ferromagnetic, and semiconductor/ferroelectric nanoheterostructures for enhancing the performance of photocatalytic processes have been discussed. Finally, key challenges and future prospects for designing more efficient photocatalytic materials are briefly outlined.
Semiconductor heterostructures have attracted intensive research attention during the past few years owing to their great potential for energy and environmental remediation related applications. Effective optical absorption and efficient separation of photogenerated charge carriers are among the key factors for achieving high efficiency in a photocatalytic process. This mini-review summarizes state-of-the-art activities in designing nanosemiconductor heterostructures using multifunctional semiconductors for solar-to-hydrogen conversion and degradation of organic pollutants. Various novel design strategies such as semiconductor/graphene heterojunctions including graphene as a semimetal and photosensitizer, semiconductor/ferromagnetic, and semiconductor/ferroelectric nanoheterostructures for enhancing the performance of photocatalytic processes have been discussed. Finally, key challenges and future prospects for designing more efficient photocatalytic materials are briefly outlined.
The worldwide growth of the population and industries has led to
an increase in environmental pollution and energy consumption which
has raised serious concerns for sustainable development of society
in the near future. Our natural water resources have been affected
severely due to the disposal of a large amount of wastewater containing
toxic organic dyes from many industrial processes such as in the textile,
plastic, leather good, cosmetics, and electroplating industries.[1] Also, burning conventional energy sources such
as coal, methane, and petroleum releases a variety of green-house
gases such as CO2, CO, and N2O, which further
pose a serious threat to the environment and eventually to human health.
Thus, there is an urgent need for efficient strategies for reducing
environmental pollution and developing clean and environmentally friendly
energy sources. Semiconductor photocatalysis using abundant solar
energy is a promising approach to deal with the energy crisis and
worsening environmental issues through the generation of hydrogen
and detoxification of organic pollutants, respectively. Hydrogen is
considered as a potential renewable energy source for the future due
to its high energy density and near-zero-emission operation which
also provide high-quality energy services in a wide range of applications.
The basic requirements for the generation of hydrogen and detoxification
of organic pollutants using semiconductor materials are nearly the
same, except for the mechanisms involved in both the processes, which
will be discussed further in a later section of this mini-review.Over the past few years, significant research efforts have been
devoted to improving the photocatalytic efficiencies of semiconductor
materials.[2] An efficient photocatalytic
process requires semiconductor materials with wide optical absorption
range, efficient charge carrier separation, and excellent chemical
stability in aqueous environments. At the beginning, a wide bandgap
semiconductor such as TiO2, as the representative photocatalytic
material, has been studied extensively. However, due to its limited
optical absorption, the need to use narrow bandgap semiconductors
to enhance the effective optical absorption range of solar energy
was eventually realized.[3] Besides, the
continuous development of visible-light-active semiconductor materials,
it is also of significant importance to enhance their chemical stability
and reduce the recombination rate of photogenerated charge carriers.
Recently, a variety of functional semiconductors such as ferroelectric,
ferromagnetic, and graphene photosensitizers have been used to address
the above-mentioned issues, and using ferroelectric materials, an
internal electric field can be produced which helps in separating
out the photogenerated charge carriers.[4,5] Similarly,
research progress in using ferromagnetic semiconductors demonstrated
improvement in the photocatalytic activity in the presence of external
magnetic fields.[6] However, it was realized
that simultaneously achieving high efficiency and stability using
a single semiconductor photocatalyst is impossible due to limited
absorption of a solar spectrum, low carrier diffusion length, and
higher recombination rate. Therefore, multicomponent semiconductor
heterostructure systems have been developed in order to overcome the
limitations of single-component semiconductor photocatalysts. Combining
two or more semiconductors with different functionalities can greatly
enhance the efficiency as well as stability of the photocatalytic
materials. Recently, interesting reviews on the development of photocatalysts
using organic semiconductor/semiconductor heterostructures,[7] facet-dependent and interfacial plane-related
photocatalytic heterostructures,[8] heterostructured
semiconductor nanowire,[9] and graphiticcarbon nitride based metal sulfide heterojunction[10] have been published.In this mini-review, we present
a succinct and critical survey
of recent advances in semiconductor heterostructures and their catalytic
application prospects utilizing semiconducting heterostructures of
multifunctional semiconductors including graphene as a photosensitizer
and ferroelectric and ferromagnetic nanostructures. Finally, we conclude
with a comprehensive discussion on the key challenges and promising
future pathways for making more efficient photocatalytic materials.
Principle of Semiconductor Photocatalysis
The mechanism
for semiconductor photocatalysis is mainly comprised
of five steps: (I) absorption, (II) excitation, (III) recombination,
(IV) migration, and (V) surface reaction with electron donors and
acceptors [Figure (a)]. Step I consists of an effective absorption of solar energy
by semiconductor material corresponding to its bandgap (Eg); step II consists of excitation of electrons from the
valence band (VB) to the conduction band (CB), thereby generating
electron–hole pairs in the semiconductors; and step III comprises
the recombination process in which the excited carriers due to their
very short lifetime come to the original states. Step III also runs
in parallel to step IV where the charge carriers in the excited states
migrate to the surface of the semiconductors. Only the successfully
migrated electrons and holes to the surface are involved in driving
the reduction and oxidation reactions, i.e., Step V. However, Step
V can have different reaction mechanisms depending upon the type of
application for which the photocatalytic process is used. In the case
of photodecomposition of organic pollutants, the holes in the VB participate
in oxidizing the water molecules (H2O) to generate hydroxyl
radicals (OH·), which are strong oxidizing agents
and can oxidize most of the organic pollutants [Figure (b)]. For hydrogen generation, the holes
in the VB of semiconductor photoelectrodes oxidize the water molecules
to generate O2, and subsequently, the electrons in the
CB reduce H2O or H+ to generate H2 [Figure. (c)]. However,
for effective water splitting, the position of the CB of the photocatalyst
material should be more negative than that of the redox potential
of H+/H2 (0 V vs NHE), and the VB position should
be more positive than the redox potential of O2/H2O (1.23 V vs NHE). Thus, theoretically, any semiconductor materials
with bandgap ≥1.23 eV and that possess the above constraints
can split water into H2 and O2. However, due
to some kinetic losses, the energy required for the water splitting
is ≥1.6 eV. In general, for both applications, the semiconducting
materials with bandgap in the visible-light region are preferred so
that the maximum part of the solar spectra can be utilized for the
photocatalytic activity.
Figure 1
Schematic diagrams showing (a) the basic principle
of a semiconductor
photocatalytic process, (b) reactions involved in the photocatalytic
degradation of organic pollutants, and (c) reaction mechanism involved
in the photocatalytic water splitting for generation of H2 and O2.
Schematic diagrams showing (a) the basic principle
of a semiconductor
photocatalytic process, (b) reactions involved in the photocatalytic
degradation of organic pollutants, and (c) reaction mechanism involved
in the photocatalytic water splitting for generation of H2 and O2.
Semiconductor
Heterostructure Systems
Depending upon the energy band positions
of the semiconductor components
forming the heterostructure, it can be categorized into three types:
Type I, Type II, and Type III heterostructures which are schematically
shown in Figure (a).
Out of these three types, the Type III band edge alignment is not
very suitable for photocatalytic applications and thus not explored
much. Although both Type I and Type II schemes have been used for
photocatalytic applications, among these two types, Type II band edge
alignment is the most preferred and widely used for achieving a high
efficiency photocatalytic process.
Figure 2
(a) Different types of semiconductor heterostructure
with their
band edge positions, (b) TEM image of the Bi2S3/CdS heterostructure,[11] (c) comparison
of the photodegradation rate of methyl red (MR) with various catalysts
(CdS NPs, Bi2S3 NW, TiO2 (P25), Bi2S3 + CdS NP, and Bi2S3/CdS
heterostructure) under UV light,[11] (d)
TEM image of CdS/ZnO/RGO nanocomposites,[14] and (e) photocatalytic degradation rate constant of MB dye using
different photocatalysts CdS, ZnO, CdS/ZnO, and CdS/ZnO/RGO.[14] Reprinted with permission from ref (11). Copyright 2011, American
Chemical Society. Reprinted with permission from ref (14). Copyright 2015, Elsevier.
(a) Different types of semiconductor heterostructure
with their
band edge positions, (b) TEM image of the Bi2S3/CdS heterostructure,[11] (c) comparison
of the photodegradation rate of methyl red (MR) with various catalysts
(CdS NPs, Bi2S3 NW, TiO2 (P25), Bi2S3 + CdS NP, and Bi2S3/CdS
heterostructure) under UV light,[11] (d)
TEM image of CdS/ZnO/RGO nanocomposites,[14] and (e) photocatalytic degradation rate constant of MB dye using
different photocatalysts CdS, ZnO, CdS/ZnO, and CdS/ZnO/RGO.[14] Reprinted with permission from ref (11). Copyright 2011, American
Chemical Society. Reprinted with permission from ref (14). Copyright 2015, Elsevier.
Type I Semiconductor Heterostructure Systems
Figure (a) schematically
describes the relative position of the band edges in the construction
of a Type I heterostructure system. The energy band positions of the
two combining semiconductor materials are such that the conduction
(CB) and valence band (VB) positions of one of the semiconductors
lie in between the energy band positons of the second semiconductor.
The separation of the photogenerated charge carriers in these types
of heterostructure systems depends upon the difference in the migration
rate of photogenerated electrons and holes at the interface. Thus,
the positions of the band edges of the combining semiconductors play
an important role in determining the enhancement in the photocatalytic
activity. Fang et al.[11] reported the synthesis
of the Bi2S3/CdS heterostructure using the wet
chemistry approach. Figure (b) shows the TEM picture of the Bi2S3/CdS nanocomposite which exhibits higher photochemical activity for
the photodegradation of methyl red under UV light irradiation due
to the improved charge carrier separation process [Figure (c)]. The band edge potentials
of Bi2S3/CdS favor the transfer of photogenerated
electrons and holes in CdS to Bi2S3; however,
the migration rate for the two types of charge carriers (i.e., electrons
and holes) is different, and this results in the enhancement in the
performance of the semiconductor heterostructure photocatalysis.In addition to the nanocomposite heterojunction, core/shell type
heterostructure systems have also shown better potential to manipulate
the charge transfer process at the interface. Depending upon the band
edge potentials of the semiconductors used for the construction of
the core/shell heterostructure, the migration of the photogenerated
electron–hole pairs can be achieved either toward the core
semiconductor or toward the shell semiconductor. Thibert et al.[12] reported a 10-fold increment in the photocatalytic
activity toward H2 evolution using a Type I CdS/CdSe core/shell
nanostructure as compared to the CdSe nanostructure alone. The enhancement
in the photocatalytic activity has been attributed to the passivation
of surface-deep trap states in the CdSe core due to the coating of
the CdS shell around it, which resulted in sufficient redox potential
of electrons in the core for the reduction of water. The electrons
in the core semiconductor also participate in the photocatalysis reaction
at the surface after tunneling through the CdS shell.
Type II Semiconductor Heterostructure Systems
Among
different strategies to enhance the efficiency of semiconductor
photocatalysis, the design of Type II heterostructure systems has
been paid maximum attention. In the Type II heterostructure system,
the conduction and valence band positions of one of the semiconductors
lie above the conduction and valence bands of the second semiconductor
[Figure (a)], which
provide an optimum pathway for improving the separation of the photogenerated
charge carriers and can efficiently enhance the photocatalytic activities.
A variety of material combinations for the design of the Type II heterostructure
are explored in the literature. Recently, 2D materials have been extensively
studied for the electrocatalytic or photocatalytic activities due
to their layered structures.[13] The electrical
and optical properties of a 2D material can be tuned by controlling
the number of layers. The synthesis of a CdS/ZnO/RGO ternary nanohybrid
for efficient photocatalytic degradation of methylene blue dye has
been demonstrated.[14]Figure (d) shows the TEM picture of trio nanohybrids.
The CdS/ZnO core/shell nanostructure after coupling with reduced grapheneoxide (RGO) exhibited much enhanced degradation of methylene blue
dye as compared to its bare counterparts such as CdS/ZnO, ZnO, or
CdS, which is due to the formation of a Type II heterostructure, resulting
in efficient transfer of photogenerated electrons from CdS to ZnO
and further to reduced graphene oxide, thus resulting in higher separation
capability of the photogenerated charge carriers [Figure (e)]. In an extension of this
work, synthesis of the CdS/CoFe2O4/RGO ternary
nanohybrid by replacing ZnO with the CoFe2O4 shell by a chemically stable and magnetic CoFe2O4 shell layer around the CdS is also reported.[15] The chemically stable CoFe2O4 shell
protects CdS from photocorrosion in aqueous solution under illumination,
and also the magnetic properties of CoFe2O4 lead
to easy separation of the composite material from the photocatalytic
reaction system for reusability.
Graphene, a two-dimensional
(2D) structure of sp2-hybridized
carbon atoms, has drawn considerable attention for electronic, photonic,
and catalytic applications due to its fascinating properties such
as high conductivity (106 S cm–1), excellent
mobility of charge carriers at room temperature (200000 cm2 V–1 S–1), and large specific
surface area (2630 m2 g–1). Pristine
graphene is a zero bandgap semimetal, and therefore it is widely used
as a conducting nanoplatform for facilitating charge transfer for
improving hydrogen production and environmental remediation activities.
On the other hand, a tunable bandgap can also be induced in graphene
by chemical doping, thereby converting it into a semiconductor[16] [Figure (a)]. To date, various semiconductor/graphene heterojunctions
including Schottky junctions and Type II heterojunctions using semimetallic
and semiconducting properties of graphene have been constructed for
photocatalytic applications.[17] Some recent
studies also make use of the optical properties of RGO to effectively
absorb the solar spectrum for enhancing the photocatalytic activities.[18]
Figure 3
(a) Left: the π* and π band dispersion of
pristine
graphene in the Brillouin zone. Right: zoom-in of the linear energy
bands at the Dirac point and the position of Fermi level for n- and
p-type doping.[16] (b) Schematic band diagram
of the graphene/semiconductor Schottky junction for photocacatlytic
H2 evolution.[20] (c) Hydrogen
production efficiency of xRGO-NiPO catalysts under
visible-light illumination.[20] (d) Schematic
energy band diagram of the CdS/CoFe2O4/RGO ternary
heterostructure.[15] (e) Rate constants for
the degradation of MB dye using CdS, CFO, CdS/CFO, and CdS/CFO/RGO
nanostructures under visible-light irradiation.[15] Reprinted with permission from ref (16). Copyright 2010 American
Chemical Society. Reprinted with permission from ref (20). Copyright 2019 American
Chemical Society. Reprinted with permission from ref (15). Copyright 2015, Royal
Society of Chemistry.
(a) Left: the π* and π band dispersion of
pristine
graphene in the Brillouin zone. Right: zoom-in of the linear energy
bands at the Dirac point and the position of Fermi level for n- and
p-type doping.[16] (b) Schematic band diagram
of the graphene/semiconductor Schottky junction for photocacatlytic
H2 evolution.[20] (c) Hydrogen
production efficiency of xRGO-NiPO catalysts under
visible-light illumination.[20] (d) Schematic
energy band diagram of the CdS/CoFe2O4/RGO ternary
heterostructure.[15] (e) Rate constants for
the degradation of MB dye using CdS, CFO, CdS/CFO, and CdS/CFO/RGO
nanostructures under visible-light irradiation.[15] Reprinted with permission from ref (16). Copyright 2010 American
Chemical Society. Reprinted with permission from ref (20). Copyright 2019 American
Chemical Society. Reprinted with permission from ref (15). Copyright 2015, Royal
Society of Chemistry.Zhang et al.[19] proposed the use of graphene
in fabricating semiconductor/graphene heterojunctions using P25 titania
for the degradation of MB dye. In a Schottky junction, graphene is
coupled to semiconductors with higher work functions, and consequently,
an upward band bending arises at the contact interface due to the
alignment of Fermi energy levels [Figure (b)]. Recently, Samal et al.[20] constructed a Schottky junction of RGO–NiPO and
demonstrated enhanced H2 production with an admirable rate
of 9000 μmol/h/g [Figure (c)]. Further, to improve interfacial charge transport of
Schottky heterojunctions, using 2Dgraphene sheets with 2D semiconductors
was also reported. For the efficient charge transfer process, the
contact area between the semiconductor and graphene sheets is also
an important parameter. In order to demonstrate this effect, Bera
et al.[21] synthesized CdS nanostructures
with different dimensionalities, i.e., zero-dimensional nanoparticels,
one-dimensional nanorods, and two-dimensional CdS nanosheets, and
coupled these nanostructures with reduced graphene oxide sheets. The
RGO coupled CdS nanosheets exhibit 4 times higher conductivity than
the CdS nanoparticle/RGO composite and 3.4 times higher than the CdS
nanorod/RGO nanocomposite. The observed enhancement is attributed
to the increase in the interfacial contact area between the CdS and
RGO using sheet-like structures of CdS. The interfacial contact between
graphenes and semiconductors is also found to depend upon the number
of graphene layers used in the formation of nanocomposites with semiconductors.Almeida et al.[22] designed a ternary
nanocomposite comprised of TiO2, Cu2O, and RGO
and showed higher photoresponse of ternary TiO2/Cu2O/RGO nanocomposites as compared to TiO2/RGO and
Cu2O/RGO nanocomposites. The photosensitization role of
RGO was initially proposed by Du et al.[23] by the ab initio calculations and demonstrated that the electrons
in the upper valence band of RGO can be directly excited to the conduction
band of TiO2 under visible-light excitation. The simulated
results were also supported with experimental observation of appreciable
visible-light response in the photocurrent density measurements of
the RGO–TiO2 nanocomposite. The chemically modified
reduced graphene oxide (RGO) can be directly used as a semiconductor
for photocatalytic applications. Singh et al.[15] also reported a visible-light responsive Type II ternary heterostructure
system using CdS/CoFe2O4/RGO for photocatalytic
degradation of methylene blue dye (Figure (d),(e)). Under visible-light irradiation,
the electrons from the conduction band of CdS are transferred to the
conduction band of CoFe2O4, and holes are transferred
from the valence band of CoFe2O4 to the valence
band of CdS. Also, due to the visible-light response of RGO and its
Fermi level position, the photoexcited electrons in RGO are transferred
to the conduction band of CoFe2O4, thereby increasing
the electron concentration in the CoFe2O4 which
improved efficient separation of the electron–hole pairs and
resulted in the enhancement in the photocatalytic activity.For effective utilization of the optical properties of RGO toward
high efficiency of the photocatalytic materials, the understanding
of the interfacial interaction between the graphene and semiconductor
is critical and needs to be addressed.
The use of ferroelectric materials as semiconductor
photocatalysts
has recently attracted a lot of attention and is considered as a new
pathway for efficient solar water splitting and degradation of organic
pollutants.[4,5] The spontaneous electrical polarization
in ferroelectrics can generate an internal electric field which helps
in the efficient separation of photogenerated charge carriers as well
as the modulation of band alignment at the semiconductor/liquid interface,
resulting in an enhanced photoconversion efficiency. Ji et al.[24] demonstrated the effect of ferroelectric polarization
on photocatalytic water splitting using epitaxial BiFeO3 thin films. A saturated photocurrent of ∼10 μA·cm–2 at 0.64 V vs Ag/AgCl and an ∼0.016 V shift
in the photocurrent onset were attained after electrical polarization.
Thereafter, tremendous research efforts have been devoted, especially,
to solar water splitting using a variety of ferroelectric films such
as NaNbO3,[25] PZT,[26] and BaTiO3,[27] either as photoanodes or photocathodes. In order to improve the
charge transport properties, ferroelectric materials at the nanoscale
with different morphologies were also fabricated. Li et al.[28] fabricated vertically aligned epitaxial KNbO3 nanowire arrays on a Nb-doped SrTiO3 substrate,
and by switching the polarization state the photocurrents were tuned
from 0.7 μA·cm–2 to 11.5 μA·cm–2 at 0 V vs Ag/AgCl [Figure (a)]. However, chemically grown nanostructures
exhibit various structural defects resulting in higher recombination
losses. Singh et al.[29] reported the growth
of an oriented, highly crystalline nanoporous structure of Ag,Nb-codoped
SrTiO3(Ag/Nb:STO) with ferroelectric properties using pulsed
laser deposition. These vertically aligned nanoporous structures exhibited
enhanced surface area and directional charge transport, resulting
in enhanced PEC properties using ferroelectric polarization. By manipulating
the external electrical bias, ∼3-fold enhancement in the photocurrent
from 40 to 130 μA·cm–2 was obtained.
Concurrently, the flat-band potential was found to decrease from −0.55
to −1.13 V, revealing a giant ferroelectric tuning of the band
alignment at the semiconductor surface, and results in the enhanced
charge transfer.
Figure 4
(a) Schematic illustration of solar water splitting reaction
on
a vertically aligned KNbO3 nanowire arrays.[28] (b) Photocurrent responses of KNbO3 nanowires with different ferroelectric polarization conditions.[28] (c) Schematic illustration of the electronic
band structure of TiO2/BaTiO3 core/shell nanowires
and the charge transfer mechanism after poling.[38] (d) Photoresponse of the as-prepared, positively poled,
and negatively poled TiO2/BaTiO3 core/shell
nanowires prepared at 210 °C.[38] (e)
Flexible PVDF/Cu/PVDF-NaNbO3 photoelectrode[39] and (f) photoresponse with different poling
conditions.[40] (g) Linear sweep voltammetry
curves of the CoFe2O4 photoanode measured with
and without a magnetic field (under 100 mW/cm2 UV–vis
illumination).[40] Reprinted with permission
from ref (28). Copyright
2017, Elsevier. Reprinted with permission from ref (38). Copyright 2015, American
Chemical Society. Reprinted with permission from ref (39). Copyright 2017, Elsevier.
Reprinted with permission from ref (40). Copyright 2018, Nature Communication.
(a) Schematic illustration of solar water splitting reaction
on
a vertically aligned KNbO3 nanowire arrays.[28] (b) Photocurrent responses of KNbO3 nanowires with different ferroelectric polarization conditions.[28] (c) Schematic illustration of the electronic
band structure of TiO2/BaTiO3 core/shell nanowires
and the charge transfer mechanism after poling.[38] (d) Photoresponse of the as-prepared, positively poled,
and negatively poled TiO2/BaTiO3 core/shell
nanowires prepared at 210 °C.[38] (e)
Flexible PVDF/Cu/PVDF-NaNbO3 photoelectrode[39] and (f) photoresponse with different poling
conditions.[40] (g) Linear sweep voltammetry
curves of the CoFe2O4 photoanode measured with
and without a magnetic field (under 100 mW/cm2 UV–vis
illumination).[40] Reprinted with permission
from ref (28). Copyright
2017, Elsevier. Reprinted with permission from ref (38). Copyright 2015, American
Chemical Society. Reprinted with permission from ref (39). Copyright 2017, Elsevier.
Reprinted with permission from ref (40). Copyright 2018, Nature Communication.Large band gaps and high dielectric constants possessed
by most
of the ferroelectric materials resulted in small photocurrents. In
order to overcome the disadvantages of poor light absorption, ferroelectric
materials were coupled with plasmonic nanostructures. Wang et al.[30] demonstrated surface plasmonic effect induced
enhancement in the PEC properties of PbZr0.2Ti0.8O3 thin films anchored with Ag nanoparticles. Further,
Cheng et al.[31] constructed a Si-pnn+/ITO/Au/BiFeO3 (BFO) hybrid photocathode catalyzed
by MoS2/Pt using visible-light active semiconductors for
efficient transfer of photogenerated electrons from Si to the electrode
surface. In the Au/BFO[32] system, the local
surface plasmonic resonance effect of Au/Ag nanoparticles and the
depolarization electric field of BFO were found to enhance the PEC
activity of the photocathode, and also the tunability in the PEC performance
was demonstrated.Ferroelectric/semiconductor heterostructure
systems which synergize
the advantages of both ferroelectric and semiconductor materials are
demonstrated to be a potential approach in achieving higher photocurrents.[33] The effect of ferroelectric polarization on
the electronic properties and band alignment at the ferroelectric/semiconductor
interface was studied by Jang et al.[34] using
the PbTiO3/TiO2 heterostructure. By using the
macroscopic average approach, it was found that the negative polar
surface at the interface favored the transfer of holes from PbTiO3 to TiO2, while the positive polar interface favored
the transfer of electrons from PbTiO3 to TiO2. Accordingly, a polarization-dependent photocatalytic performance
for the degradation of organic pollutants and hydrogen evolution reaction
was demonstrated. Cheng et al.[35] fabricated
a Si-pn+/ITO/PZT photocathode for hydrogen generation.
An enhancement in the photocurrent from −100 μA·cm–2 to −1.2 mA·cm–2 (at
0 V vs RHE) was demonstrated due to the depolarization electric field
generated in the PZT film which helped in driving the photogenerated
charge carriers from the Si-pn+ junction to PZT. Xie et
al.[36] demonstrated that by using ferroelectric
BiFeO3 as a passivation layer for the BiVO4 photoanode
an efficient and stable solar water oxidation performance can be realized.
Furthermore, due to the ferroelectric properties of BiFeO3, the PEC performance of the composite photoanode can be manipulated
based on the direction of self-polarization in BiFeO3.
The charge recombination rate was found to be decreased from 17 s–1 to 0.6 s–1. A polarization-dependent
photocatalytic performance was also demonstrated combining multiple
photocatalysts in a Z-scheme system. An enhanced transfer of the charge
carriers was attained by inserting a ferroelectric material (i.e.,
BiFeO3) with downward band bending between BiVO4 and CuInS2 photocatalysts. Consequently, a 2-fold enhancement
in the photocurrent and ∼16-fold enhancement in the photocatalytic
degradation rate of 4-nitrophenol were reported.[37]In order to effectively collect the photoexcited
charge carriers
generated in the semiconductors, nanoscale ferroelectric/semiconductor
heterostructure systems were fabricated. For the core/shell nanostructures
of TiO2/BaTiO3, spontaneous electrical polarization
in the ferroelectric layer significantly improved the charge separation
efficiency, leading to ∼67% enhancement in the photocurrents,
respectively[38] (Figure (c) and (d)). A few efforts in designing
flexible ferroelectric/semiconductor photoelectrodes were also made
for the commercial viability of PEC technology. Singh et al.[39] fabricated a large area flexible PVDF/Cu/PVDF-NaNbO3 photoelectrode with ferroelectric properties and demonstrated
an enhanced photocurrent of ∼1.37 mA/cm2 with electric
field polarization (Figure (e),(f)). Using a similar concept of ferroelectric materials,
few researchers have also used ferromagnetic materials to modify the
charge transport properties of semiconductors using external magnetic
fields. Singh et al.[40] fabricated the CoFe2O4 photoanode and demonstrated enhanced photoelectrochemical
properties under low external magnetic fields [Figure (g)], which has been attributed to a magneto-phototronic
effect. However, further efforts in understanding the exact mechanism
for the enhanced PEC properties are required.
Conclusions
and Future Perspectives
In this mini-review, a comprehensive
overview of the current achievements
in preparing nanoheterojunction photocatalysts using multifunctional
semiconductors such as graphene, ferroelectric, and ferromagnetic
materials, and their design strategies including fundamental aspects
in constructing various semiconductor heterostructure systems for
photocatalytic H2 evolution and degradation of organic
pollutants are discussed. Graphene-based heterostructures including
Schottky junctions and Type II heterostructures are also thoroughly
highlighted and discussed. Inclusion of ferroelectric and ferromagnetic
in nanoheterostructures provides the opportunity to achieve higher
charge transfer efficiency through electrical/magnetic tunneling.
Extensive research progress has been achieved in the formation of
semiconductor heterostructures; however, for practical applications
and commercialization of heterostructure photocatalysts, further research
efforts are required in designing more efficient and stable heterostructure
photocatalysts. For future research directions in this exciting and
highly rewarding field, the following aspects can be highlighted.Good interfacial
contact between different
combining layers in multicomponent heterostructure systems is very
much required. Thus, further progress in preparing heterojunction
photocatalysts with interfacial engineering for achieving suitable
band alignment and efficient charge transport properties and also
exploring new visible-light-active photocatalyst materials with proper
band alignment can be a promising strategy.Fabricating heterostructure photocatalysts
using multifunctional semiconductors such as ferroelectric and ferromagnetic
materials is a promising strategy for achieving high efficiency. However,
systematic studies using advanced spectroscopic techniques are required
to understand the migration pathways of the photogenerated charge
carriers. Further, theoretical calculations and modeling methods are
required for a deep understanding of the charge migration kinetics
at the interface.