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This journal is c The Royal Society of Chemistry 2012 Chem. Commun., 2012, 48, 10369–10385 10369
Cite this: Chem. Commun., 2012, 48, 10369–10385
Chemical and biological sensors based on metal oxide nanostructures
Yoon-Bong Hahn,*ab
Rafiq Ahmadwa and Nirmalya Tripathywa
Received 2nd July 2012, Accepted 8th August 2012
DOI: 10.1039/c2cc34706g
Unique and fascinating features of metal oxide nanostructures (MONs) have attracted
considerable attention in recent years because without much effort, the MONs can be grown in
many different nanoscale forms, thus allowing various novel devices of chemical and biological
sensing to be fabricated. To improve the sensors performance by tailoring the properties of
MONs through engineering of morphology, particle size, effective surface area, functionality,
adsorption capability and electron-transfer properties have been extensively explored. This feature
article collates the various MONs and their potential applications in the chemical and biological
sensors for clinical and non-clinical applications.
1. Introduction
Compared with the various traditional analytical systems,
sensors have been acknowledged as relevant tools for detection
and quantification of several biochemical compounds, chemicals,
minerals, etc. Sensors are the devices composed of active
sensing materials coupled with a signal transducer. These
devices transmit the signal from a change in reaction or
selective compound and thus produce a signal (such as electrical,
thermal or optical output signals) which is converted into
digital signals for further processing. Thus the very selection
and development of a potential active material play a key role
in designing efficient, reliable and innovative sensing devices.
Moreover, recent developments in the field of nanotechnology
and materials science have paved the way for synthesis of
numerous new materials with desired morphologies and
physical–chemical properties. In particular, MONs among
various types of engineered nanomaterials have received
enormous attention for their promising sensing applications.1
The MONs are found to exhibit several unique features such
as controllable size, functional biocompatibility, bio-safe,
chemical stability, and catalytic properties. In addition, they
possess enhanced electron-transfer kinetics and strong adsorp-
tion capability with a wide range of available information
about the chemical modification of their surfaces, makes them
more advantageous over other conventional materials on account
of electron transfer and immobilization of biomolecules
aDept. of BIN Fusion Technology, Chonbuk National University,567 Baekje-daero, Deokjin-gu, Jeonju 561-756, Republic of Korea
b School of Semiconductor and Chemical Engineering, andSemiconductor Physics Research Center, Chonbuk NationalUniversity, 567 Baekje-daero, Deokjin-gu, Jeonju 561-756,Republic of Korea. E-mail: [email protected]
Yoon-Bong Hahn
Yoon-Bong Hahn is a WCUprofessor in the Department ofBIN Fusion Technology andSchool of Semiconductor andChemical Engineering, ChonbukNational University, Korea.He is also the Director ofNational Leading ResearchLaboratory for Hybrid GreenEnergy Development. Hereceived his BS from HanyangUniversity, MS from SeoulNational University, and PhDfrom University of Utah,U.S.A. His main researchactivities focus on the
synthesis of metal and metal oxide nanostructures and theirapplications for chemical and biological sensors, optoelectronicdevices, and solar cells.
Rafiq Ahmad
Rafiq Ahmad received his BSc(Honors) in Zoology fromAMU and MSc degree inBiotechnology from KIITBhubaneswar, India in 2005and 2009, respectively. Nowhe is pursuing his PhD underProfessor Hahn’s guidance atthe Department of BIN FusionTechnology, Chonbuk NationalUniversity, Korea. His currentresearch interest includessynthesis of metal and metaloxide nanomaterials bysolution process and develop-ment of biosensors, chemicalsensors and hybrid sensors.
w RA and NT equally contributed to this work.
ChemComm Dynamic Article Links
www.rsc.org/chemcomm FEATURE ARTICLE
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10370 Chem. Commun., 2012, 48, 10369–10385 This journal is c The Royal Society of Chemistry 2012
for enhanced chemical and biological sensor performances,
respectively.2 In fact, MONs were also preferred as optical
emitters, electronic conductors, catalysts, carriers for ampli-
fied detection signal and biosensing interface, etc.
Various MONs such as zinc oxide, iron oxide, cerium oxide,
tin oxide, zirconium oxide, titanium oxide and magnesium
oxide, etc. have been extensively evaluated for their potential
in chemical and biological sensing applications. The various
synthesized nanostructural forms of these metal oxides including
nanoparticles (NPs), nanotubes (NTs), nanowires (NWs), nano-
rods (NRs), nanobelts, nanosheets, nanotips, quantum dots
(QDs), hollow spheres, etc. were achieved through sol–gel
synthesis,3 hydrothermal or solvothermal growth,4 physical or
chemical vapour deposition,5 low temperature aqueous growth,6
chemical bath deposition,7 or electrochemical deposition.8
Moreover, the amalgamation of conducting and semiconducting
NPs/QDs such as gold, silver, platinum, carbon nanotubes,
graphene etc. is reported to enhance the optical, electrical and
magnetic properties of the MONs, thereby resulting in
improved selectivity, stability and sensing performances.
Hence, smart selection, design and application of MONs will
lead to a new generation of sensing devices exhibiting novel
function with enhanced signal amplification and coding stra-
tegies that may address future economic and social needs.
A review article on this topic is timely, with a large number
of studies reported on both chemical and biological sensors
using MONs and increase in their commercial attentions.9 In
this feature article, the focus sheds light on recent research
developments made over last five years in synthesis of MONs
and their use in fabricating sensing devices by reviewing
published works. Basically, this article reviews the use of
various MONs for chemical and biological sensors, and the
prospective on the future development of sensors and their real
time usages for economic and social benefits.
2. Chemical sensors based on metal oxide
nanostructures
Chemical sensors, with recent significant developments for
detection and quantification of chemical species, are becoming
an enabling technology in a wide range of applications such as
clinical, industrial, agricultural and military technologies
thereby resulting in social and economic benefits. Fig. 1
illustrates a fundamental working principle of chemical sensors.
A chemical sensor is defined as a small device where a chemical
interaction occurs between the analyte gas and/or liquid and
the sensor device, transforming chemical or biochemical
information of a quantitative or qualitative type into an
analytically useful signal. The signal from a sensor is typically
electronic in nature, being a current, voltage, or impedance/
conductance change caused by electron exchange. These
devices contain a physical transducer and a chemically sensitive
layer or recognition layer. Chemical sensors can be character-
ized by several features such as stability, selectivity, sensitivity,
response and recovery time, and saturation.10
The MONs as chemical sensing materials have been exten-
sively studied for a long time due to their advantageous
features such as good sensitivity to the ambient conditions
and simplicity in fabrication.11 The basic concept behind
employing a metal oxide is that when an oxide is held at
elevated temperatures, the surrounding gases react with the
oxygen in the oxide causing changes in the surface potential
and resistivity of the material. Additionally they were also well
recognized as substrates, electrodes, promoters, structure
modifiers, membranes and filters for successful fabrication of
chemical sensors. Moreover, the metal oxide based chemical
sensors can be produced in arrays allowing sensing of multiple
species simultaneously along with advances in sensitivity and
low detection limits around part-per-million (ppm) levels for
some species.
Recently, several works have demonstrated the usage of
different MONs with their optimized characteristics for the
development of innovative chemical sensing devices including
Fig. 1 Schematic showing the working principles of chemical sensors.
Nirmalya Tripathy
Nirmalya Tripathy receivedher BSc (Honors) in Botanyfrom OUAT and MSc inBiotechnology from KIITBhubaneswar, India in 2007and 2009, respectively. Pre-sently she is pursuing herPhD under Professor Hahn’sguidance at the Department ofBIN Fusion Technology,Chonbuk National University,Korea. Her current research issynthesis of metal and metaloxide nanomaterials bysolution process and theirapplication in biological fieldssuch as drug delivery systemsand antibacterial agents, etc.
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This journal is c The Royal Society of Chemistry 2012 Chem. Commun., 2012, 48, 10369–10385 10371
Table 1 Comparison of performances of MON-based chemical sensors
Materials Target speciesLowestdetection conc.
Sensor response/temperature
Response/recovery Ref.
SnO2 NW H2 10 ppm B0.4/300 1C N/A 122-Propanol 0.5 ppm –/RT* N/A 13
SnO2 hollow spheres CO 50 ppm –/300–350 1C o1 min/30 min 14SnO2 nanocrystals NO2 100 ppb –/RT* 15SnO2 Porous NPs H2/CO 160/200 ppm –/300 1C N/A 16SnO2 flower-like CO 50 ppm B2.13/350 1C 26 s/34 s 17SnO2 NRs H2 100 ppm B13/150 1C N/A 20Polypyrrole-coated SnO2 hollow spheres NH3 3 ppm –/RT* 15 s/several min 21Plasma-modified SnO2 NWs Ethanol 100 ppm –/250 1C N/A 22Pt@SnO2 NRs Ethanol 10 ppm 3.7/300 1C 2 s/20 s 23NiO-doped SnO2 polyhedra Ethanol 30 ppm 6.7/280 1C 0.6 s/10 s 24NiO-SnO2 nanofibers Ethanol 100 ppm 25.5/300 1C 2 s/3 s 25Ni-SnO2 hollow spheres Ethanol 5 ppm 5.4/300 1C 1–3 s/1–3 min 26NiO-SnO2 nanofibers Toluene 50 ppm B2/330 1C 11.2 s/4 s 27Hollow NiO-SnO2 nanospheres NH3 20 ppm 32.3/300 1C 0.5 s/4 s 28p-NiO/n-SnO2 Heterojunction Composite Nanofibers H2 100 ppm 13.6/320 1C B3 s/B3 s 29ZnO NRs Ethanol 1 ppb B10/300 1C 100 s/– 34ZnO NRs Methanol 50 ppm 11.8/300 1C 3 s/9 s 35
Xylene 50 ppm 9.6/150 1C 6 s/12 sZnO NR-bundle and nanoparticle thin films Ethanol 100 ppm B20/320 1C 10 s/5 s 36Single ZnO NW H2 200 ppb B0.04/RT 30 s/50–90 s 37ZnO NW NO2 0.5 ppm –/225 1C –/– 38ZnO NRs arrays H2 500 ppm –/250 1C 6 min/17 min 41Single ZnO NW H2 10 ppm –/RT 3 s/2 s 42Multiple ZnO NWs H2 50 ppm –/200 1C –/– 43Pt adsorbed single crystalline ZnO NWs NH3 1000 ppm –/350 1C 100 s/100 s 44ZnO NPs Ethanol 1000 ppm 25/370 1C –/– 45ZnO NRs Ethanol 1 ppm –/370 1C 10 s/10 s 46
Benzene 50 ppb –/370 1C –/–ZnO flower-like CO 10 ppm –/200 1C –/– 47ZnO films Methane, H2 100 ppm –/150 1C 150 s/400 s 48Necked ZnO NPs NO2 0.2 ppm 100/200 1C 13 s/10 s 49Co-doped ZnO NRs CO 50 ppm –/350 1C –/– 50
Ethanol 1.5 ppm –/350 1C –/–Au-doped ZnO NWs Ethanol 1000 ppm B36/240 1C –/– 51Al-doped ZnO nanomaterials Ethanol 3000 ppm B200 B8 s/B10 s 52Pd nanodots-functionalized ZnO NW CO 100 ppb 1.02/20 1C 120 s/180 s 53Ga2O3 NW O2 1% O2 4.75/300 1C –/– 55
CO 200 ppm 3.95/200 1C –/–NiO NTs Ethanol 200 ppm 22.6/250 1C –/– 57a-Fe2O3 hollow spheres Ethanol 10 ppm B5/RT –/– 58
Formaldehyde 10 ppm B3/RT –/–Fe2TiO5/a-Fe2O3 nanocomposite Ethanol 10 ppm B10/320 1C 28 s/21 s 59WO3 NWs H2S 1 ppm 48/250 1C –/– 60WO3 NWs NH3 10 ppm –/RT –/– 61WO3 Nanoplates Ethanol 10 ppm B1.9/300 1C –/– 62CuO NWs CO 30 ppm B0.07/300 1C –/– 63
NO2 2 ppm B0.15/300 1C –/–CuO nanoribbons Methanol 5 ppm B1.4/RT 2–4 s/3–7 s 64
Ethanol 5 ppm B1.2/200 1C 3–6 s/4–9 sPorous CuO NWs H2 6% H2 407%/250 1C 72 s/156 s 65CdO NWs NO2 1 ppm B0.27/100 1C –/– 66Nd2O2CO3 NPs CO2 300 ppm –/25 1C –/– 67ZnSnO3 NRs H2 500 ppm o2.2/RT –/– 68Co3O4 hollow spheres Butanol 10 ppm 3/100 1C 1–3 s/4–8 s 69Co3O4 NRs Acetone 223 666 2664%/300 1C 24 s/180 s 70
Benzene 149 111 2236%/300 1C 15.6 s/120 sEthanol 74 570 1850%/300 1C 18.6 s/150 s
Fe2O3–TiO2 tube-like nanostructures Ethanol 500 ppm 8.2/270 1C –/– 71In2O3 nanofibers Ethanol 100 ppm B14/300 1C 1 s/5 s 72aIn2O3 NPs NOx 200 ppm B10 000/150 1C –/– 72bSn-doped In2O3 nanopowders CO 50 ppm 4/250 1C –/– 72cIn2O3 hollow micro spheres Ethanol 100 ppm 137.2/400 1C –/– 72dIn2O3 porous nanoplatelets Ethanol 5 ppm 5.8/22–28 1C 1–3 s/3–5 s 72eAg-doped In2O3 nano particles Alcohol vapors 100 ppm –/150 1C 42 s/34 s 72fIn2O3 NRs Formaldehyde 32 ppm –/300 1C 276 s/65 s 72gMesoporous In2O3 NRs Ethanol 500 ppb 1.71/290 1C 6 s/8 s 72hIn2O3 NP film H2S 20 ppb –/RT –/– 72iPt/In2O3 nanofibers H2S 600 ppm 1490/200 1C 60 s/120 s 72jAu-In2O3 NWs CO 0.2 ppm 104/RT B130 s/B50 s 72kNano-In2O3 Ethanol 20 ppm 14.7/300 1C –/– 72l
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SnO2, ZnO, In2O3, Ga2O3, V2O5, ZnSnO3, Wo3, etc. Herein
we have categorized chemical sensors depending on the type of
metal oxide used for detection of various target species. Below
the recent works on chemical sensors based on MONs12–72
have been reviewed and summarized in Table 1.
2.1. SnO2 nanostructure-based chemical sensors
Tin oxide (SnO2), highly sensitive and fast-responding metal
oxide, has undergone an extensive research for the elaboration
of chemical sensors targeting various gases. Various morpho-
logies of nano-SnO2 have been exploited such as NWs, hollow
spheres, nanocrystals, etc. for selective or multiple detection of
chemicals. Wang et al. showed that the SnO2 NW based sensor
can detect hydrogen (H2) concentration in the range of 10 to
1000 ppm, attributed to the under coordinated atoms on the
SnO2 NWs surfaces.12 Likewise SnO2 nanowires and hollow
nanospheres,13,14 SnO2 nanocrystals,15 nanocrystalline porous
SnO216 showed promising sensing behaviours towards CO,
NO2, and H2, respectively. Interestingly, researchers also
discovered the multiple sensing capabilities of SnO2 nano-
structure. For example, hierarchical three dimensional flower-
like SnO2 nanospheres were shown to exhibit a good response
and reversibility for CO, methane, methanol, and ethanol.17
Also SnO2 nanopolyhedrons (assembled from ultrathin SnO2
NWs) were configured as high performance sensors to detect
methanol, ethanol, and acetone, exhibiting 1 ppm sensitivity,
fast response and recovery times (several seconds for different
gases with concentrations of 1–200 ppm) to all the target gases
and highly selective detection to acetone.18 In a comparative
study, Brunet et al. concluded that SnO2 NW sensors have
higher detection efficiencies, i.e. more than 30 times than the
SnO2 thin film sensor towards CO, CH4, H2, CO2, SO2 and
H2S, attributed to a lack of grain boundaries.19 In the case of
the thin film sensor with larger exposed surface area (800 times),
a single detected electron requires B2760 gas molecules
impinging the sensor surface whereas the single NW sensor
requires only B86 gas molecules.
Taking one step ahead, scientists endeavoured to improve the
sensors performances by demonstrating some modified version
of SnO2 employing methods like doping or by synthesizing
composites, etc. In this regard, several remarkable works come
into picture including faster response and higher sensitivity of
polypyrrole-coated SnO2 hollow spheres for ammonia detec-
tion,21 higher sensitivity of plasma modified SnO2 NWs22 and
uniformly loaded Pt@SnO2 NRs23 for ethanol gas at lower
operating temperatures, attributed to the increased concen-
tration of oxygen vacancies on SnO2 NWs surface and to both
the chemical and the electrical contribution of Pt, respectively.
Further p-NiO/n-SnO2 heterojunction nanofiber based sensors,
proposed by Wang et al.,29 show excellent H2 sensing properties
such as high sensitivity and fast response-recovery (B3 s)
behaviour with the detection limit of approximate 5 ppm H2
at 320 1C, especially for SnO2 nanofibers containing 4.11
mole% NiO. Hwang et al. have displayed a 3.7-fold enhance-
ment in gas response of SnO2 NWs decorated by discontinuous
Ag NPs towards 100 ppm ethanol at 450 1C compared to
pristine SnO2 NWs, explained by the increase in resistance in air
via the electronic interaction between Ag and SnO2 NWs.30
Similarly, based on the density functional theory Wei and
co-workers studied the effect of Cu-doping on SnO2 sensitivity
and the adsorption properties of H2S on SnO2 (110) surface.31
They suggested that Cu-doping can directly improve the
formation of surface oxygen vacancies in SnO2, and the
formation energy is in relation to Cu depth from surface.
Recently, based on the online in situ photoelectron spectro-
scopic detection technique Li et al.32 proposed a new model
for a Pd-doped SnO2 based CO gas sensor.
They found that the surface lattice oxygen and the bulk
lattice oxygen of SnO2 are involved in the CO-sensing process;
Pd works as the transport carrier for CO, whereas the surface
oxygen of SnO2 is the transport carrier for oxygen. Also
Hwang et al. have suggested a facile and eloquent route for
large scale fabrication of single crystalline SnO2 NWs network
sensors for the selective detection of NO2 and ethanol.33
2.2. ZnO nanostructure-based chemical sensors
Zinc oxide (ZnO) nanostructure based chemical sensors have
recently aroused much interest owing to easy synthesis, and
distinctive optical, electrical and chemical sensing properties.
In general, ZnO NR or NW based sensors were exploited
by many research groups for sensing of various chemicals
(Hahn et al., Chao et al., Yang et al., Ge et al., Lupan et al.,
Ahn et al.). Hahn et al., for the first time, demonstrated the
fabrication of hydrazine electrochemical sensor using ZnO
nanonails (Fig. 2).39a The sensor showed a high and reprodu-
cible sensitivity of 8.56 mA mM�1 cm�2 with a response time
less than 5 s, a linear range from 0.1 to 1.2 mM and detection
limit of 0.2 mM. Likewise, they also reported a successful and
efficient fabrication of hydrazine sensors employing ZnO NRs
and high aspect ratio ZnO NWs.39b,c
Further, several nano/micro structured ZnO have been
focused for designing hydrazine sensors such as nanoflowers,
NPs, etc.40 Hahn et al. also reported a method for measuring
the electrical characteristics of aligned ZnO NR arrays
Fig. 2 Low (a) and high (b) magnification SEM images; (c) cyclic
voltammetric sweep curve for the Nafion/ZnO/Au electrode without
hydrazine (solid line) and with 1 mM N2H4 (dashed line) in 0.01 M
PBS (pH = 7.4). The scan rate was 100 mV s�1; (d) amperometric
response of the Nafion/ZnO/Au electrode with successive addition of
hydrazine in the range of 0.5 to +0.4 V; and (e) plot of 1/i vs. 1/C.
Reprinted with permission from ref. 39a. Copyright r 2008 RSC.
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This journal is c The Royal Society of Chemistry 2012 Chem. Commun., 2012, 48, 10369–10385 10373
(NRAs) directly grown on a pre-patterned four-point probe
system in solution, without any additional processing (Fig. 3).41
This ZnO NRAs device was used for detecting H2, exhibiting
an increased sensitivity with the increase in H2 concentration
and the operating temperature. Interestingly, the multiple gas
sensing behaviour of ZnO NW based chemical sensors was
also examined towards H2, NH3, i-butane, and CH4 at room
temperature. The study showed that the ZnO NW is suitable
for nanoscale sensor applications because of its capability to
operate at room temperature, ability to tune the gas response,
and high selectivity.42 In a comparative study between single
and multiple NW gas sensors, Khan et al. reported the effect of
nanojunctions in multiple ZnO NW sensors for H2 detection.43
Recently, Tian et al. demonstrated ZnO NRs thin film gas
sensors by a solution processing technique. It was found that
the enhanced performance is attributed to the exposed facet
suggesting that the surface structure at the atomic level is a key
factor in improving the oxygen adsorption and, consequently,
the gas-sensing performance of a ZnO NRs array based gas
sensor.46
Li et al.50 reported a low temperature synthesis of Co-doped
ZnO NRs on ITO substrates and patterned Al2O3 substrates,
the schematic plots for the fabrication process of sensors are
depicted in Fig. 4(a). The fabricated sensor at different CO
concentrations exhibits fast response and high sensitivity
(Fig. 4b), where Co-doped ZnO sensors show improved
sensitivity compared with undoped ZnO. This approach of
adding impurity into semiconducting NRs is effective in
improving sensing properties and can be applied to other
semiconducting NRs as well. Furthermore, to enhance the
sensing response the ZnO nanostructures were functionalized
with metal catalysts such as Au, Pt and Pd. The metal dopant
acts as a catalyst to modify the surface reactions of metal oxide
semiconductors toward sensing gases. The Au-doped ZnO
NW based sensor showed a higher sensitivity than the
undoped based sensor with an optimum operating tempera-
ture of 240 1C.51 The Al-doped ZnO sensor also showed an
excellent sensitivity (B200) with short response time (B8 s)
and recovery time (B10 s) to 3000 ppm ethanol.52 Recently,
Choi and Kim have reported an improvement in sensitivity
using Pd nanodots-functionalized ZnO NWs for sub-ppm CO
sensing, ascribed to the combined effect of electronic and
chemical sensitizations due to the Pd NPs.53
2.3. Other metal oxide based chemical sensors
For chemical sensors, selectivity is of great importance for
practical applications. Hence, several novel MONs based gas
sensors were being focused in search of a suitable material
having broad sensing capabilities such as detecting toxic gases
and trace components in gas mixtures with high selectivity.
Gallium oxide (Ga2O3) nanostructures, being chemically and
thermally stable metal oxide with low cross-sensitivity to
humidity, slight O2 deficiency and incomplete crystallinity,
are more preferable for high temperature sensing applications
such as chemical, environmental, and explosives gas sensors.54
A gas sensor based on Ga2O3 NWs dispensed on an inter-
digitated Pt-electrode showed reversible response to O2 and
CO at 100–500 1C along with peak responses at 300 1C for O2
and 200 1C for CO. The sensor response increases empirically
with gas concentrations.55 Yan et al. reported mesoporous
single crystal Ga2O3 nanoplates by heating a single crystal
nanoplate of GaOOH, demonstrating potential applications in
fluorescence markers and gas sensitivity in detecting CO.56
Recently, a crystalline meso-/macroporous Co3O4 NR
based sensor was fabricated using a facile hydrothermal
Fig. 3 (A) Schematic diagram showing fabrication process of the
electrodes; (i–iv) low and high magnification FESEM images of ZnO
NRs arrays selectively grown without an electrode and (v–viii) ZnO
NR arrays grown directly on a four point probe; (C) dynamic
responses of the patterned ZnO NR arrays to H2 pulses at 250 1C;
and (D) sensitivity at various operating temperatures. Reprinted with
permission from ref. 41. Copyright r 2010 Elsevier B.V.
Fig. 4 (a) Schematic drawing of the fabrication of sensors; (b) the
time-dependent resistance of continuous exposure to CO (50 ppm,
150 ppm, 350 ppm, and 750 ppm) ambient at 350 1C. (b) The
sensitivities of undoped, 0.76 at%, and 1.85 at% Co-doped ZnO
sensors at different CO concentrations. Reprinted with permission
from ref. 50. Copyright r 2012 Elsevier B.V.
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method from CoCl2 and urea precursors, without additional
agents for detection of benzene, acetone, and ethanol. The
sensor exhibits good stability, high sensitivity (7.1 folds and 4
folds higher than that of NPs and porous plates, respectively),
fast response and recovery times along with a highest sensitivity
for acetone with fast response and recovery times of one
minute, attributed to the carrier (reference) gases and pre-
adsorbed oxygen (Fig. 5).70 The Fe2O3–TiO2 tube-like nano-
structure based sensor, in which TiO2 shell is of quasi-single
crystalline characteristic and its thickness can be controlled
through adjusting the added amount of aqueous Ti(SO4)2solution.71 These nanostructures exhibit enhanced ethanol
sensing properties with respect to the monocomponent
suggesting a novel type of nanostructure for fabrication of
nanodevices. In addition, various types of In2O3 nanostructure
based chemical sensors were fabricated for sensing NH3, CO,
H2S, NOx, ethanol, formaldehyde, and alcohol vapors.72
3. Biological sensors based on metal oxide
nanostructures
By definition, a biological sensor or a biosensor is a miniaturized
analytical device comprising an analyte and a biological
receptor layer coupled with a transducer for signal evaluation,
either directly or through a mediator. The specific biological
receptor layer is a biocatalytic sensing element (e.g., antibody,
enzyme, receptor protein, nucleic acid, whole cell/tissue section),
capable of recognizing its specific analyte (compound whose
concentration is to be determined), and regulating the
specificity and sensitivity of a biosensor. The main aim of a
biosensor is to generate either discrete or continuous digital
electronic signals that are proportional to analyte, evaluated
with physicochemical transducers such as optical, electro-
chemical, and micro gravimetric or calorimetric (Fig. 6). Because
of their low cost fabrication, specificity, rapid response time,
portability and easy access, biosensors are powerful analytical
tools for clinical diagnosis.
In the fabrication of a biosensor device, the key issue to
improve the selectivity and sensitivity of the sensor is by
maintaining the activity of the immobilized biomolecules
which are obviously affected by pH, temperature, humidity
and toxic chemicals. Since the biosensor performance mostly
depends on the immobilizing matrices and/or supporting
materials, various conventional immobilizing matrices such
as either inert metals (for example, platinum and gold) or
carbon-based materials were extensively studied. However, the
various conventional methods face certain limitations such as
inability to precisely control the transducer and other materials
used in the biosensors construction, complicated synthesis
protocols and sensor fabrication, nonspecific binding of other
molecules and low sensitivity to peroxide, as well as to other
mediators, etc. Hence, the MONs are promising materials for
sensing applications due to various intriguing features. In
particular, their biomimetic, fast electron communication,
high surface to volume ratio, modified-surface work function,
high surface reactivity, high catalytic efficiency, strong adsorp-
tion ability and effectiveness in retaining the biomolecule
activity make them excellent candidates for immobilization
purposes. Hence, selecting the best MON suitable for desired
biomolecules immobilization is another crucial point as the
nano-bio interfaces between MONs and immobilized bio-
molecules determine the effectiveness of the biosensor. This
nano-biointerface is influenced by various factors such as
surface area and charge, roughness and porosity, functional
groups, valence/conductance states, hygroscopic nature, physical
states, etc. of the MON. In general, the attachment of bio-
molecules on to the MONs surface is achieved via physical
adsorption, entrapment, crosslinking, covalent coupling and
encapsulation. The established nano-biointerface provides
high stability, preserves the biomolecules by establishing
a biocompatible microenvironment, and demonstrates an
excellent selectivity when coupled to bio-recognition molecules
with simple design.
Biosensors, in a more advanced and sophisticated form, specia-
lized for real time monitoring are known as ‘wearable’ biosensors.
Fig. 5 Electrical and gas sensing properties of meso-macro porous
Co3O4 NR based gas sensor: (a) ethanol sensing measured at different
temperatures using N2 as reference; and (b) ethanol sensing measured
at different temperatures using dry air as reference. Gas sensing
properties of porous Co3O4 NRs to acetone, ethanol, and benzene
measured at 300 1C: (a) the change in sensor resistance upon exposure
to different concentrations of acetone, ethanol, and benzene and (b)
sensor response as a function of gas concentration; ((b)-inset) the
response to benzene of NPs, meso-/macroporous NRs and porous
plates (plates). Reprinted with permission from ref. 70. Copyright r
2011 American Chemical Society.
Fig. 6 Schematic showing the working principles of biological sensors.
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A wearable biosensor continuously monitors the physiological
signals, collects sensor data, communicates the sensed data by
wireless strategies, and analyses the data in real time as a
person leads their normal lifestyle activities. This biosensor
can be worn in various positions such as wrist watches, shirts,
smart phones, spectacles, etc., supporting integrated motion,
skin conductance, and temperature sensors in a small wearable
package. Various advantages of such ‘wearable’ biosensors
include rapid continuous monitoring, detection of transient
phenomena, easy to use, and accuracy. Herein, we have
reviewed some of the promising MON-based biosensors
depending on the biomolecules immobilized on their surfaces
including enzymes and several other biomolecules. The
different types of reported MON-based biosensors are
discussed and summarized.
3.1. Enzyme immobilized biological sensors
3.1.1. Glucose oxidase immobilized biosensors. Glucose
biosensors are the most studied among all biosensors, where
the MONs with high isoelectric point (IEP) have been conti-
nuously chosen for the glucose oxidase (GOx) immobilization
with low IEP of 4.2.73 Further modified versions of glucose
biosensors with enhanced performances were achieved by
using various nanostructures and their composites with
desired biopolymers. Nanostructured ZnO, with a high IEP
of 9.5, exhibits a high electron transfer rate, enabling high
enzyme loading and fast electron transfer between the GOx
immobilized site and the electrode. The GOx integrated
nanostructured ZnO such as NPs, NRs, nanotubes, nano-
plates, nano-tetrapods, nanonails, etc., grown and transferred
on supporting electrodes have shown to be highly selective,
sensitive towards glucose with fast response time. Table 2
shows the performance comparison of glucose biosensors
based on different types of nanostructure mediators.74–112
A highly sensitive amperometric biosensor based on a single
ZnO nanofiber synthesized by electrospinning has been shown
to have high and reproducible sensitivity of 70.2 mAmM�1 cm�2
for continuous glucose monitoring with an enhanced thermal
stability at 20–85 1C (Fig. 7).74 Fang et al. designed Nafion/
GOx/ZnO hollow nanospheres on a GCE electrode,
display good sensitivity (65.82 mA mM�1 cm�2) and fast
response time (o5 s) because of the higher surface area of
ZnO hollow nanospheres and high GOx adsorption.75
Improving the stability of biosensors without loss of sensitivity
or selectivity is one of the biggest challenges for glucose
monitoring. In this regard, researchers focused on synthesizing
various composites and doped ZnO. Yang et al. have fabri-
cated glucose biosensors employing ZnO/Cu nanocomposites
for GOx immobilization, where direct electron transfer of
GOx is achieved at ZnO/Cu nanocomposites with a high
heterogeneous electron transfer rate constant of 0.67 � 0.06 s�1
providing a matrix for direct electrochemistry of enzymes and
mediator-free enzymatic biosensors.90 Likewise hexagonal
ZnO NRs and nanoflakes have been focused for GOx adsorp-
tion on the tip of a silver-covered borosilicate glass capillary
and borosilicate glass capillary, respectively, for intracellular
glucose measurements in human adipocytes and frog
oocytes.91 Other MONs were also studies for improving
glucose biosensor performances by enhancing GOx loading
such as CuO, CeO2, Fe3O4, MgO, etc. Hahn et al. have shown
a highly sensitive amperometric glucose biosensor using CuO
nano-flower composed of nanosheets.101 The high GOx affi-
nity to glucose is assigned to the biocompatible nature, high
specific surface area, chemical stability, and conductivity,
enables direct electron transfer of the CuO nanostructures in
the Au/CuO/GOx/Nafion electrode surface. Similarly, MgO
based polyhedral nanocages and nanocrystals were employed
for the fabrication of glucose biosensors with high and
reproducible sensitivity of 31.6 mA mM�1 cm�2 with a response
time of less than 5 s, a linear dynamic range of 1.0–9.0 mMand a detection limit as low as 68.3 � 0.02 nM.108 Recently,
Patil et al. fabricated a glucose biosensor based on CeO2 NRs
and GOx, exhibits a linear range for the detection of glucose
from 2 to 26 mM, a reasonably good and reproducible sensitivity
of 0.165 mAmM�1 cm�2, with a response time of 1–2 s, a 100 mMlimit of detection and good anti-interference ability.104
3.1.2. Cholesterol oxidase immobilized biosensors. In order
to fabricate an efficient and reliable cholesterol biosensor,
various MONs have been studied for the immobilization and
stabilization of cholesterol oxidase (ChOx). Table 3 shows the
performance comparison of cholesterol biosensors fabricated
with different types of nanostructures modified electrodes.113–126
Hahn et al. have designed highly-sensitive cholesterol bio-
sensors based on ChOx immobilization on well-crystallized
ZnO nano-flowers113 and ZnO NPs114 grown by a low temp-
erature simple solution process. These biosensors showed a
very high, reproducible sensitivity and low detection limit with
response time o5 s. Similarly, cholesterol biosensors were
fabricated using nano-ZnO films115 and nanoporous ZnO thin
films,116 providing a better environment and enhanced
electron transfer between ChOx and electrode. Further
improved sensitivity with a low Km value cholesterol biosensor
was became prominent with the use of composites, platinum–
gold hybrid functionalized ZnO NRs117 and Pt-incorporated
ZnO nanospheres,119 etc. However, most research groups not
only used expensive gold (Au) or platinum (Pt) electrodes, but
also synthesized nanostructures on substrates then transferred
and coated them onto electrodes, requiring additional proces-
sing. Hence mitigating such huddles, for the first time, Hahn
et al. have reported the use of aspect ratio (AR)-controlled
ZnO NRs which were grown directly on a silver electrode in
solution at 90 1C for the fabrication of cholesterol biosensors
(Fig. 8).120 The biosensor with AR = 60 ZnO NRs exhibits a
high reproducible sensitivity of 74.10 mA mM�1 cm�2, a low
detection limit of 0.0015 mM, a linear response up to 16.0 mM
with fast response time (o2 s). They concluded that the higher
sensitivity and faster response time with higher AR is mainly
due to higher specific surface area of ZnO NRs enabling high
enzymes loading on ZnO NRs arrays and direct faster electron
communication between the ZnO NRs and the Si/Ag electrode.
A cholesterol biosensor based on the nanocomposite film of
nano-CeO2 and chitosan (CH) has been also reported by
Malhotra et al., exhibiting increased electro active surface
area for ChOx loading, enhanced electron transport between
ChOx and electrode with improved biosensor performance.121
Similarly, Ansari et al. have used SnO2 NPs and chitosan
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composite film for ChOx immobilization and reported a high
sensitivity of the biosensor attributed to high adsorption
ability, improved electrocatalytic activity and good bio-
compatibility of the CH-SnO2/ITO nanocomposite.124 Many
other MONs were also targeted for ChOx adsorption and
fabrication of sensitive cholesterol biosensors such as electro-
deposited CoOx NPs125 and nano-Fe3O4.126
With all these innovative MONs-based platforms for high
ChOx loading, it would be very interesting to further modify
the MON based cholesterol biosensors for total quantification
of cholesterol concentration and real time monitoring of
cholesterol.
3.1.3. Horseradish peroxidase immobilized biosensors. Like
above explained biosensors, the MONs were found to be
excellent platforms for horseradish peroxidase (HRP) immo-
bilization and sensing of hydrogen peroxide (H2O2), a com-
pound of particular importance in biological systems. Table 4
summarizes the performance of the HRP immobilized bio-
sensors for sensing H2O2.127–145A flower-like ZnO-gold
NP-Nafion nanocomposite for effective HRP adsorption
was reported for H2O2 sensing via direct electron transfer.
This matrix provides a favourable microenvironment for the
enzyme to retain its activity as the sensor demonstrates a
linear response over a wide range of H2O2 concentration
(15–1100 mM), a detection limit of 9.0 mM and rapid
response.130 Yang et al. have proposed a novel biosensor based
on the ZnO/CHIT inorganic organic composite film using
complex multiple nano-fork like ZnO for HRP immobilization.133
The as-prepared biosensor showed ultrahigh sensitivity
(201.12 mA mM�1), quick response, low detection limit
(0.3 mM) and small apparent KM value (0.292 mM). Thus,
the complex multiple nano-fork like ZnO is a promising
material for promoting the electron transfer of proteins and
constructing enzymatic biosensors. Likewise, ZnO NRs were
fabricated on gold wire by hydrothermal reaction without
any surfactant, where a Zn–Au alloy thin layer was coated
on gold wire end to improve the nucleation for growth of ZnO
NRs. An improved performance was achieved by alternate
immobilization of poly(sodium-4-styrenesulfonate) and HRP
onto ZnO for H2O2 detection without an electron transfer
mediator.131
A bioelectrode based on a HRP immobilized nanostructured
CeO2 matrix via a physiosorption technique, exhibits a linearity
over the range 1.0–170 mM and a low KM (22.1 mM) for H2O2
detection.134 A similar approach has been used to fabricate an
Table 2 Comparison of performances of Glucose oxidase immobilized biosensors
Working electrodesSensitivity(mA mM�1 cm�2)
KappM
(mM)Detectionlimit (mM)
Linearrange (mM)
Response time (s)/potential (V) Ref.
GCE/ZnO NF/PVA/GOx/L-Cys 70.2 2.19 1 0.25–19 o4/+0.80 74GCE /ZnO-HNSPs/GOx/Nafion 65.82 — 1 0.005–13.15 o5/+0.8 75GCE/ZnO NRs/GOx/CHIT 25.7 1.95 10 0.01–0.25/0.3–0.7 o2/+0.8 76ITO glass/ZnO NRs film/GOx/Nafion — — 3 0.005–0.30 o5/+1.0 77Au/ZnO NT/GOx/Nafion 21.7 19 1 0.05–12.0 3/+0.8 78Au/transferred ZnO NRs/GOx/Nafion 15.46 3.097 50 0.05–5.45 B10/+0.8 79Au/grown ZnO NRs/GOx/Nafion 23.43 2.749 10 0.01–5.9 B7/+0.8Au/ZnO nano-tetrapods/GOx/Nafion 25.3 5.05 4 0.005–6.5 o6/+0.8 80ITO/ZnO NT arrays/GOx/Nafion 30.85 2.59 10 0.01–4.2 o6/+0.80 81Au/ZnO nanonails/GOx/Nafion 24.613 14.7 5 0.1–7.1 o10/+0.80 82PET/Au/ZnO-NWs/GOx/Nafion 19.5 1.57 o50 0.2–2.0 o5/+0.80 83GCE/ZnO/Au/GOx/Nafion 1492 0.41 0.01 0.0001–0.033 o5/+0.55 84ITO/ZnO/(PSS/PDDA)3/GOx/Nafion — 3.12 1.94 0.1–9.0 o4/�0.2 85GCE/TPSP-ZnO/GOD/Nafion — — 10 0.05–8.2 o5/�0.5 86GCE /MWCNTs/GOx ZnO/GOx 10.03 2.48 2.22 0.00667–1.29 –/�0.30 87PDDA/GOx/ZnO/MWNTs 50.2 — 0.25 0.1–16 –/– 88Ti/C-ZnO/GOD/Nafion 35.3 B1.54 1 0.01–1.6 B5/�0.45 89ITO/Cu/ZnO/HRP-GOx/Con A/CS-Au 0.097 1.47 40 1.0–15.0 o6/�0.39 90GCE/porous TiO2/GOx/Nafion 0.3 — — 0.15–1.2 o10/�0.45 92GCE/1DHS TiO2/GOx/Nafion 9.9 1.54 1.29 Up to 1.5 o5/�0.45 93FTO/TiO2/H2BpybcBr2/GOx 1.25 3.76 51 0.153–1.3 /+0.55 94Ti/TiO2NT/AuNPs/MAA/GOD — 7.2 310 0.4–8.0 o10/�0.25 95TiO2/CNT/Pt/GOx 0.24 — 5.7 0.006–1.5 o3/+0.40 96ITO/TiO2-SWCNT/GOx 5.32 0.83 10 0.01–1.4 o9/�0.25 97GCE/f-TiO2-Pt NPs/GOx/CS — 18.2 0.25 0.00125–3.0 �/+0.65 98GCE/TiO2-GR/GOx 6.2 — — 0–8.0 –/�0.60 99Ti/TiO2 NTA/Ni 200 — B4 0.1–1.7 �/+0.55 100Au/CuO/GOx/Nafion 47.19 8.7 1.37 0.01–10.0 o5/� 101GCE/CuO nanospindles/GOx/Nafion 5.5675 — 1 0.001–0.80 �/+0.45 102Au/CeO2/GOx 0.00287 13.55 12 2.78–11.10 o5/� 103ITO/CeO2 NRs/GOx 0.165 44.57 100 2.0–26.0 1–2/+0.80 104Pt/nanoporous CeO2/GOx — 1.01 — 1.39–8.33 �/+0.33 105Pt/GOx/Fe3O4/Chitosan/Nafion 11.54 0.611 6 0.006–2.2 –/– 106ITO/CH-Fe3O4/GOx 9.3 0.141 50 0.5–22.0 B5/– 107Au/MgO/GOx/Nafion 31.6 0.0343 0.068 0.001–0.009 o5/ 108GCE/NH2-TiO2-CNT/GOx 7.0 8.59 0.44 0.0018–0.266 3/�0.35 109GCE/NiFe2O4/GOx/CHIT 45.6 — — 1–8.0 o4/+0.6 110Pt/NiO doped ZnONRs/GOx 61.78 7.4 2.5 0.5–8.0 o5/+0.39 111GCE/NiO/GOx/CHIT 3.43 7.76 47 1.5–7 o8/+0. 112
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amperometric H2O2 biosensor based on electrochemically
deposited PANI–CeO2 nanocomposite films onto ITO electrode.137
Further several other CeO2 morphologies like single crystal
CeO2 nanocubes, Au/CeO2-chitosan composite based H2O2
biosensors were prepared, providing direct electron transfer
and electrocatalysis of horseradish peroxidase.135,136
Furthermore, novel and interesting remodelled MONs were
synthesized for more precise and accurate H2O2 detection such
as nano-MgO, SnO2 NRs, Sb-doped, ZrO2, RuNPs, etc. In
this regard, Lu et al. developed nano-MgO and chitosan
composite based sensor for H2O2 detection in the presence
of hydroquinone as a mediator.138 Owing to excellent electro-
catalytic behaviour of MgO, this sensor demonstrates a linear
range of 10�4–1.3 mM with a detection limit of 0.05 mM. In a
comparative study, a mediator-free HRP adsorbed biosensor
based on Sb-doped SnO2 NWs provides excellent electron
transfer for the enzymes and higher electroactivity toward
H2O2 than undoped SnO2 NWs.141
3.1.4. Urease and glutamate dehydrogenase immobilized
biosensors. Recently, Ali et al. have fabricated a urea biosensor
based on urease (Urs) immobilized ZnO NW arrays, shows
sensitivity of 52.8 mV per decade and a linear range of
0.1–100 mM.146 Also, a bioelectrode based on the Urs-
immobilized TiO2 film exhibited a shorter response time (25 s),
a wider linear range (8 mM-3 mM), a lower detection limit
(5.0 mM) and good stability (with about 93.3% of the original
response signal retained after 1 month).147 Further high
affinities of Urs and glutamate dehydrogenase (GLDH) for a
nanobiocomposite film of superparamagnetic Fe3O4 NPs
Fig. 7 (a) Schematic of electrospinning experimental setup used for
the fabrication of ZONFs, (b) SEM image of the as-prepared NF, (c)
cyclic voltammograms of the bare and modified gold electrode without
and with 100 mM glucose in pH 7.0 PB solution (inset – schematic
diagram of the modified gold electrode), and (d) amperometric
response of the biosensor based on ZONF to different concentrations
of glucose at 0.8 V in a stirring pH 7.0 PB solution (Inset-bottom
right). Reprinted with permission from ref. 74. Copyright r 2010
American Chemical Society.
Table 3 Cholesterol oxidase immobilized biosensors
Working electrodes SensitivityKappM
(mM)Detectionlimit (mM)
Linearrange (mM)
Response time (s)/applied potential (V) Ref.
Au/flower-shaped ZnO/ChOx/Nafion 61.7 mA mM�1 cm2 2.57 0.012 1.0–15.0 o5/� 113Au/ZnO NPs/ChOx/Nafion 23.7 mA mM�1 cm2 B4.7 0.00037 0.001–0.5 o5/+0.355 114ITO/Nano-ZnO/ChOx 2.296 mA mM�1 cm2 0.0256 0.013 0.13–10.36 10/� 115Au/Nanoporous ZnO/ChOx — B2.1 — 0.65–10.34 B15/+0.50 116GCE/CS-MWCNTs/Pt–Au@ZnONRs/ChOx 26.8 mA mM�1 1.84 0.03 0.0001–0.076 o6/+0.45 117Ag/ZnO/ChOx 35.2 mV per decade — — 0.001–10.0 –/– 118GCE/Pt ZnO NS/ChOx/Nafion 1886.4 mA mM�1 cm2 — — 0.5–15.0 o5/+0.20 119Si/Ag/Ag/ZnO NRs (AR = 15)/ChOx/Nafion 30.94 mA mM�1 cm2 0.34 0.0035 0.02–11.0 o5/+0.38 120Si/Ag/Ag/ZnO NRs (AR = 30)/ChOx/Nafion 54.24 mA mM�1 cm2 0.20 0.0022 0.01–14.0 o5/+0.38Si/Ag/Ag/ZnO NRs (AR = 60)/ChOx/Nafion 74.1 mA mM�1 cm2 0.16 0.0015 0.01–16.0 o2/+0.38ITO/Nano ZnO-CHIT/ChOx 141 mA mg dL�1 0.221 — 0.13–10.36 15/� 121ITO/NS-CeO2/ChOx 2 mA mg dL�1 cm2 1.953 — 0.26–10.36 B15/+0.50 122ITO/CH-NanoCeO2/ChOx 47 mA mg dL�1 cm2 0.09 0.13 0.26–10.36 10/� 123ITO/CH-SnO2/ChOx 34.7 mA mg dL�1 cm2 3.8 130 0.26–10.36 0.5/� 124GCE/CoOx NPs/ChOx 0.0435 mA mM�1 cm2 0.49 4.2 0.0042–0.050 15/+0.80 125ITO/NanoFe3O4/ChOx 86 O mg�1 dL cm�2 0.02 6.5 0.0065–10.36 25/+0.06 126
Fig. 8 (a) Schematic illustration for the fabrication of the biosensors;
(b) histograms showing the relationship between the enzyme immobi-
lization percentage and the aspect ratio of ZnO NRs with growth time;
(c) amperometric responses of the aspect-ratio dependent biosensors
to successive addition of cholesterol solution in 0.1 M PBS (pH 7.4) at
an applied potential of +0.38 V; and (d) calibration curves for
the response current vs. cholesterol concentration of the fabricated
biosensors. Reprinted with permission from ref. 120. Copyright r
2012 Elsevier B.V.
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and chitosan was observed to a low Km of 0.56 mM.148 A
bioelectrode based on co-immobilized Urs and GLDH nano-
structured ZnO composite shows a high sensitivity and a
detection limit of 13.5 mg dL�1 with Km of 6.1 mg dL�1,
indicating a good affinity of Urs-GLDH for urea.149 Similarly,
an improved biosensing characteristic was reported for ZnO
and CH nanocomposites, assigned to their high electroactive
surface area and combined effect of CH and ZnO NPs resulting
in increased loading of Urs-GLDH and improved charge
transport.150 This biosensor exhibited a high linearity and low
KM (4.92 mg dL�1) due to enhanced affinity of enzymes toward
the nanobiocomposite. It will be useful to utilize these sensors
for reliable detection of urea concentration in real samples.
3.1.5. Lipase immobilized biosensors. Only a very few
MONs have received attention for lipase immobilization to
fabricate biosensors. Solanki et al. reported a nanostuctured
cerium oxide (35 nm) film for Lipase immobilization, exhibiting
high affinity for tributyrin with linearity of 50–500 mg dL�1,
detection limit (32.8 mg dL�1), shelf life of 12 weeks, and low
Km value obtained as 22.27 mg dL�1 (0.736 mM).151 Similarly,
lipase adsorbed magnetic nickel-ferrite NPs at the gate of an
ion-selective field-effect transistor to quantify tributyrin, tri-
octanoate and triolein concentrations in the range of 0.1–1.5%.152
3.1.6. Other enzymes immobilized biosensors. Luo et al.
reported highly conductive TiO2 nanoneedle film for cyto-
chrome complex (cyt c) immobilization, facilitating the
electron transfer between redox enzymes and electrodes.153
This study also highlights the inherent enzymatic activity
toward H2O2 released from human liver cancer cells. Similarly,
various structures of nano-MnO2, i.e. amorphous MnO2,
a-MnO2 NPs and b-MnO2 NWs were electrochemically
deposited on a GCE with CH hydrogel and choline oxidase
has been developed for choline detection. Under amperometric
measurement conditions, a quicker response was monitored
for sensors based on crystalline MnO2 than those based on
amorphous MnO2. The biosensing behaviour was determined
by the specific surface area, the amount of MnO2 trapped on
the electrodes, the crystalline structure and dimensionality.
Such biosensors exhibit a linear range of 2.0–580 mM for
a-MnO2 NPs and 1.0–790 mM for b-MnO2 NWs with detec-
tion limits of 1.0 and 0.3 mM, respectively. A highly sensitive
electrochemiluminescence (ECL) lactate biosensor was
also fabricated using nano-hybrids of nanoZnO-MWCNTs
modified with lactate oxidase and Nafion.154 The sensor
showed two linear dynamic ranges of 0.01–10 mmol dL�1
and 10–200 mmol dL�1, detection limit of 4 nmol dL�1
(S/N = 3) The proposed ECL lactate biosensor was used for
determination of lactate in human blood plasma samples with
satisfactory results.
3.2. Nucleic acid immobilized biological sensors
Recently, nucleic acid immobilized MON based biosensors for
DNA detection have received tremendous attention from
researchers with the realization of its powerful capability to
convert the hybridization event into an analytical signal (see
Table 5).156–167 These DNA biosensors contain high specificity
to target sequences in the presence of non-complementary
strands and show enormous potential for detection of
diseases and genetic disorders, drug screening and forensic
applications.155 Mostly studies were concerned with their
optimized fabrication and specific applications. Zhang et al.
reported a novel DNA biosensor for acute promyelocytic
leukemia developed by immobilizing a PML/RARA related
18-mer oligonucleotides ssDNA sequence on carbon ionic
liquid electrode modified with nanosized ZnO. The bioelectrode
exhibited a detection range of 1 � 10�8 � 1 � 10�12 M and a
detection limit of 2.5� 10�13 M.159 Wang et al. also reported a
DNA biosensor based on ZnO NWs, multiwalled carbon
nanotubes (MWCNTs) and gold NPs for the detection of
sequence-specific target DNA. The single-stranded DNA probe
with a thiol group at the end (HS-ssDNA) was covalently
immobilized on the Au NPs surface by Au–S bonds. This
DNA biosensor can detect the DNA quantitatively in the range
of 1.0 � 10�13 to 1.0 � 10�7 M, with a detection limit of 3.5 �10�14 M using [Ru(NH3)6]
3+ as an intercalator.157
Table 4 Comparison of performances of horseradish peroxidase immobilized biosensors
Working electrodesSensitivity(mA mM�1 cm�2)
KappM
(mM)Detectionlimit (mM)
Linearrange (mM)
Response time (s)/potential (V) Ref.
GCE/nano-ZnO/HRP — — 11.5 0.015–15.0 –/– 127GCE/MWNTs/nano-ZnO/HRP — — 0.5 0.099–2.9 o5/�0.11 128GCE/ZnO-Chitosan/Nano Au-HRP 369.0 — 0.7 0.0015–0.45 10/�0.20 129GCE/ZnO-GNPs-Nafion-HRP — 1.76 9.0 0.00015–1.0 o5/�0.30 130Au/ZnO NR/HRP/PSS 36.28 0.01–0.026 1.9–2.5 0.005–1.7 o5/�0.25 131Ti/C-ZnO/HRP/Nafion 237.8 — 0.2 0.001–0.40 4/�0.40 132GC/fork like ZnO/CHIT/HRP 201.12 0.292 0.3 0.05–0.7 5/�0.10 133ITO/NanoCeO2/HRP 8.44 0.0221 — 0.001–0.17 3/+0.30 134GCE/Chit/CeO2/HRP — 0.00074 0.26 0.001–0.15 –/– 135GCE/CeO2-CS/Au/HRP — 1.93 7.0 0.05–2.5 –/�0.40 136HRP/PANI-CeO2/ITO 0.1596 2.9 50 000 50–500 –/– 137Au/Chit/nano-MgO/HRP 243.1 1.33 0.05 0.0001–1.30 o10/�0.10 138Au/MgO/HRP/Nafion 335.4 0.57 0.3 0.001–0.45 4/�0.10 139GCE/SnO2 NRs/HRP/Nafion 379.0 0.0339 0.2 0.0008–0.035 –/�0.47 140GCE/Sb-doped SnO2/HRP 100.0 0.76 0.8 0.01–0.45 B5/�0.30 141Au/ZrO2-HRP — 8.01 2.0 0.02–9.45 o10/�0.30 142Ti/TiO2/Au/HRP — — 2.0 0.01–0.40 o5/�0.60 143SPE/m-silica/Fe3O4/HRP 84.4 — 0.43 0.002–0.024 �/+0.50 144GCE/RuNPs/Chi-GAD/HRP 0.798 5.06 0.1 5.09–15.0 5/�0.30 145
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A nanostructured ZrO2 film electrochemically deposited on
gold surface has been used for the immobilization of 21-mer
ssDNA specific to Mycobacterium tuberculosis, demonstrates
an early and rapid diagnosis with a detection limit of
65 ng mL�1 within 60 s.160 Likewise, a DNA biosensor has
been fabricated via immobilization of 17 base ssDNA identi-
fied from the 16s rRNA coding region of Escherichia coli onto
sol–gel derived nanostructured ZrO2 film, achieving a high
selectivity and sensitivity for hybridization, with linearity in
the range of 10�6 to 106 pM of complementary DNA.162 A
DNA biosensor based on well-dispersed Cu2O hollow micro-
spheres of Cu2O NPs synthesized in aqueous solution at 25 1C
with polyvinylpyrrolidone as a surfactant, has been used for
hepatitis B virus detection.163 Further covalently immobiliza-
tion 24-mer peptide nucleic acid on 3-glycidoxypropyltri-
methoxysilane and Fe3O4 NPs nanocomposite film based
biosensor demonstrated an improvement in sensitivity and
detection limit (0.1 fM) for M. tuberculosis detection within
90 s.166 Recently, Sun et al. reported the fabrication of a stable
DNA biosensor using V2O5 nanobelts, MWCNTs and
chitosan nanocomposite materials modified carbon ionic
liquid electrode (CILE) for the immobilization of ssDNA
probes for the detection of Yersinia enterocolitica, using
DPV with methylene blue. This sensor was able to detect
specific complementary DNA at concentrations of 0.01–1.000 nM
with a detection limit of 1.76 pM.164
3.3. Antibody immobilized immunosensors
Electrochemical immunosensors, performing immunoassays
based on antigen and antibody recognition, have become vital
for the detection of determination of biochemical targets
relating to health concerns spanning from cancer antigens in
patient serum to bacterial species in food.168 The MONs
endow with surface charged nanoporous morphology and
efficient electron transfer catalytic properties, provide useful
solid support for antibody immobilization and simultaneously
enhance the electrochemical and analytical capabilities of the
electrode. Table 6 summarizes the performance of the MON-
based antibody immobilized immunosensors.169–182 Che et al.
reported an AFP sensor based on anti-AFP immobilization on
the Au NPs surfaces electrodeposited on a CH-MnO2/
MWNT-Ag composite on a GCE.169 This immunosensor is
capable of detecting AFP in the range of 0.25–250 ng mL�1
with a detection limit of 0.08 ng mL�1, assigned to high
surface area and MWCNT-Ag conductivity. Moreover the
CH-MnO2 composite film prevents the leakage and with gold
NPs provides a congenial microenvironment for anti-AFP.
Similarly, AFP sensors are reported using TiO2 NPs-CH
nanocomposite film170 and Au NWs-ZnO NRs composite
film171 on GCE for anti-AFP immobilization. The former
sensor recognizes AFP in serum amperometrically with a
linear range of 1.0–160 ng mL�1 and a low detection limit of
0.1 ng mL�1 whereas the latter can detect AFP ranging from
0.5 to 160.0 ng mL�1 with a detection limit of 0.1 ng mL�1.
Recently, Ra et al. have reported a biosensor for the real-
time, label-free detection of liver cancer markers using anti-
AFP antibody immobilized ZnO/PAC NW FET (Fig. 9).172
They demonstrated the use of ZnO NW FET act as a pH
sensor in solution for 24 h. Based on the ZnO NW FET with
solution instability, the polymer-like amorphous carbon
(PAC) nanosheets provide a multifunctional platform for
chemical and biological applications in various aspects of
solution permeability, electrochemical properties in solution,
and biomolecule immobilization via additional functionalization.
Kaushik et al. reported immunosensors for food borne
mycotoxin [ochratoxin-A (OTA)] detection employing various
combinations of MONs.173–177 Electrochemical studies of
these sensors improved sensing characteristics such as enhanced
linearity, low detection limit and fast response time. Wei
et al.179 developed an electrochemical immunosensor based
on dumbbell-like Au–Fe3O4 NPs for the detection of cancer
Table 5 Comparison of performances of nucleic acid immobilized biological sensors
Matrix for nucleic acidimmobilization Target Detection method Detection limit Detection range Ref.
ssDNA/ZnO/MWNTs/CHIT/GCE
DNA DPV with MB as indicator 2.8 � 10�12 mol L�1 1.0 � 10�11 � 1.0 �10�6 mol L�1
156
ssDNA/AuNPs/MWNTs/ZnO NWs/GCE
DNA DPV) with [Ru(NH3)6]3+ as
signaling molecule3.5 � 10�14 M 1.0 � 10�13 � 1.0 �
10�7 M157
DNA-nsZnO/ITO Genomic DNA (M. tuberculosis) DPV with MB as indicator 1 � 10�12 M 1 � 10�6 � 1 � 10�12
M158
ssDNA/ZnO/CILE PML/RARA fusion gene inacute promyelocytic leukemia
DPV with MB as indicator 2.5 � 10�13 mol L�1 1.0 � 10�12 � 1.0 �10�8 mol L�1
159
ssDNA/ZrO2/Au Genomic DNA (M. tuberculosis) DPV with MB as indicator 1 ng mL�1 1–150 ng mL�1 160ssDNA/ZrO2-CPE DNA DPV with MB as indicator r 2 � 10�10 M 2.25 � 10�10 � 2.25 �
10�7 M161
ssDNA/NanoZrO2/ITO DNA (E. coli) DPV with MB as indicator 10�6 pM 10�6 � 106 pM 162ssDNA/Cu2O/CPE DNA DPV with MB as indicator 1.0 � 10�10 mol L�1 1.0 � 10�10 � 1 �
10�6 mol L�1163
ssDNA/Chitosan-V2O5-MWCNTs/CILE
DNA (Yersinia enterocolitica) DPV with MB as indicator 1.76 � 10�12 molL�1
1.0 � 10�11 � 1.0 �10�6 mol L�1
164
ssDNA/CeO2-SWNTs-BMIMPF6/GCE
DNA of the PEPCase gene EIS with [Fe(CN)6]3�/4� as
indicator2.3� 10�13 mol L�1 1.0 � 10�12 � 1.0 �
10�7 mol L�1165
ssCT-DNA/CH-Fe3O4/ITO Cypermehtirn DPV with MB as indicator 0.0025 ppm 0.0025–2 ppm 166ssCT-DNA/CH-Fe3O4/ITO Permethrin DPV with MB as indicator 0.0025 ppm 1–300 ppmPNA/Fe3O4-GOPS/ITO Genomic DNA (M.
tuberculosis)EIS with [Fe(CN)6]
3�/4� asindicator
0.1 � 10�15 M 0.1 � 10�15 � 50.0 �10�15 M
167
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biomarker prostate specific antigen (PSA) by immobilizing
primary anti-PSA antibodies on a graphene surface and
secondary anti-PSA antibodies on Au–Fe3O4 NPs. They
showed a wide linear range (0.01–10 ng mL�1), low detection
limit (5 pg mL�1), good reproducibility, and stability.
Similarly, Gu et al. employed ZnO QDs as electrochemical
and fluorescent labels for a sandwich-type sensitive immuno-
sensor prepared by functionalizing Si substrates and perform-
ing immunoreaction of antibodies and antigens for efficient
detection of carbohydrate antigen, label for pancreatic
cancer.181 The sensor presented enhanced analytical charac-
teristics such as higher sensitivity of 0.47 mA U�1 mL�1,
broader linear range of 0.1–180 U mL�1, and lower detection
limit of 0.04 U mL�1 as well as promising results for ampli-
fication of response, stability, reliability and reproducibility.
3.4. Other biomaterial immobilized biological sensors
Based on complementary metal oxide semiconductor (CMOS)
technology, fabrication of bioelectrode was demonstrated by
Graham et al.183 In this case, the individual microelectrodes
are addressable using on-chip circuits and can meet the
requirements for long-term and non-invasive cell culture as-
says and label-free high content screening. The bioelectrode
used to sense both the fast electrical activity of neurons and
the slow changes in impedance of growing and dividing cells.
Also using a prokaryotic real-time gene expression profiling
method, Gou et al. assessed the mechanistic toxicity of nano-
structured silver and TiO2 anatase, where the properties of
compound-specific and concentration-sensitive two-dimensional
(genes and time) gene expression using nanostructured TiO2.184
4. Issues for chemical and biological sensors
Advances in nanotechnology with a broad range of engineered
MONs and multisource information fusion have expanded the
sensing world giving new horizons for addressing critical
challenges in fabricating a reliable, affordable and effective
sensor. But still their applications face several limitations
which need to be solved. A major issue is the unique signature
produced by the sensor system, i.e. selectivity of the response.
This response is based on the precise chemical and/or physical
properties of the analyte. The detection target for chemical
sensor is toxic industrial chemicals, whereas for biological
sensor is a variety of potential molecular targets – DNA,
RNA, proteins, or other metabolites. Another daunting issue
is the ability of a sensor to detect the analyte (in trace
amounts) present in complex backgrounds (soil, seawater,
body fluids, etc.). The real-world backgrounds are miscellaneous
Table 6 Comparison of performances of antibody immobilized immunosensors
Antibody immobilized matrixTarget(antigen)
Detectionmethods Sensitivity
Detectionlimit
Detectionrange of target Ref.
BSA/anti-AFP/CH-MnO2/MWNT-Ag/GCE
AFP CV — 0.08 ng mL�1 0.25–250 ng mL�1 169
a-1-fetoprotein/TiO2 NPs/CHIT/GCE AFP CV — 0.1 ng mL�1 1.0–160.0 ng mL�1 170AFP(Ab)/CH/ZnO NRs/Au NWs/GCE AFP CV — 0.1 ng mL�1 0.5–160.0 ng mL�1 171Anti-AFP Ab/ZnO-PAC NWs/FET AFP I–V — — 10–10 000 ng mL�1 172BSA/r-IgGs/Nano-ZnO/ITO Mycotoxin EIS 189 O nM�1 dm�3 cm�2 0.006 nM dm�3 0.006–0.01 nM dm�3 173IgGs/CH-Fe3O4/ITO Mycotoxin DPV 36 mA ng�1 dL�1 cm2 0.5 ng dL�1 0.5–6 ng dL�1 174BSA/r-IgGs/nanoCeO2/ITO Mycotoxin CV 1.27 mA ng�1 dL�1 cm2 0.25 ng dL�1 0.5–6 ng dL�1 175BSA/r-IgGs/CH-NanoSiO2/ITO Mycotoxin CV 18 mA ng�1 dL�1 cm2 0.3 ng dL�1 0.5–6 ng dL�1 176BSA/r-IgGs/CH-NanoCeO2 /ITO Mycotoxin CV 18 mA ng�1 dL�1 cm2 0.25 ng dL�1 0.25–6.0 ng dL�1 177Anti-CEA/Fe3O4 NRs/CPE CEA Potentiometry — 0.9 ng mL�1 1.5–80 ng mL�1 178Au-Fe3O4/Anti-PSA-Ab2/Anti-PSAAb1-GS/GCE
PSA Amperometric — 5 pg mL�1 0.01–10 ng mL�1 179
Biot-sc Ab/Streptavicin coated IronNPs/Neutravidin/glutaraldehyde/aminothiol/Au
Biotin CV 1871 O cm�2 mg mL�1 500 pg mL�1 0.5–50 ng mL�1 180
Carbohydrate 19-9 Ab/ZnO QDs/GCE Carbohydrate19–9
CV 0.47 mA U�1 mL�1 0.04 U mL�1 0.1–180 U mL�1 181
HRP-anti-hIgGAu/SiO2NPsPTHGCE H IgG CV — 0.035 ng mL�1 0.1–200 ng mL�1 182
Fig. 9 AFP bioimmobilization and electrical characterization of
amino functionalized ZnO/PAC NW. (a) Schematic diagram of the
sandwich binding method used to examine the AFP immobilization
and antibody orientations. After the sandwich binding of the anti-
AFP antibody labeled with TRITC immobilization, the fluorescence
microscopy images of the (b) untreated ZnO/PAC NW using AFP
antigen, (c) amino functionalized ZnO/PAC NW using AFP antigen,
and (d) amino functionalized ZnO/PAC NW using the serum of a liver
carcinoma patent instead of the AFP antigen. (e) Schematic illustrating
electrolyte-gated ZnO/PAC NW FET for electrical characterization.
(f) Transfer characteristics of the electrolytegated ZnO/PAC NW FET
according to AFP-related biomolecules immobilizations. Reprinted
with permission from ref. 172. Copyright r 2012 American Chemical
Society.
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and highly variable that can affect the sensor performance
unpredictably (e.g., limit of detection, response or recovery
time). An approach to minimize the effects of varying back-
grounds is to separate the analyte from backgrounds by
sample preparation. Hence, the development of a rapid, auto-
mated sample preparation protocol has become a major
technology challenge. Further, the analytical results obtained
from a sensor system should have a sufficient precision for the
specific analyte, i.e. random errors must be below a certain
limit. Hence, the repetitive determinations will be reproducible
within a certain range. A sensor should be able to detect with
accuracy close to the expected value, as one sample greatly
differs from the other, resulting in systematic errors. Thus,
sufficient standards and samples should be employed for
repeatable results/values of sufficient accuracy over an extended
period of time. Sensor lifetime and accurate reproducibility are
also important factors for medical and commercial purposes.
In general, sensors with the most robust electrodes tend to
deteriorate over a period of time or after months of use. This
depletion of electrodes performances is attributed to an expo-
sure to various reactants, pH, temperature, and humidity. Thus,
deciding the exact time for sensor recalibration to maintain its
specific accuracy can be a problem. Hence, before launching to
the market, every sensor should be consistently monitored over
sufficient period of time.
In the case of chemical sensor, the MONs being inherently
non-specific are mostly preferred for simultaneous detection of
different known chemicals as well as several unknown atmo-
spheric hazards thereby reducing concerning cost and power
consumptions. However, this technique is somewhat specific,
the use of MONs is also coupled with some disadvantages such
as some other chemicals with common characteristics may
react at different levels and get detected, generating false
positives and false alarms. This may lead to needless shut
down of equipment and evacuation of personnel. Also, the
output of MON-based chemical sensors logarithmically varies
with the chemical/gas concentrations which limit the accuracy
and linear range of the sensor. Additionally, the sensor
performance is affected by the O2 concentration, humidity,
and temperature. Especially for biological sensors, some other
important factors that affect the sensor performance are the
improvement of protein immobilization, and the long-term
stability of biochemical for storage, calibration and reprodu-
cibility. Moreover, it would be very interesting to evaluate the
effects of MONs size and toxicity in a variety of application
being clinical or non-clinical.
5. Conclusion and future prospective
Chemical and biological sensors based on MONs endow an
ambit for various innovative and novel functions with a
variety of desired applications in clinical and non-clinical
areas. New strategies including doping with electronically
active materials, functionalization of MONs with unique
groups, etc. for sensor development, have proved to be more
advantageous over traditional sensors in terms of high sensi-
tivity, super selectivity, fast response, low detect limit and
device size. As the usage of MONs for sensor designing is still
in the burgeoning stage, the future interdisciplinary researches
are envisioned to explore a new generation of sensing devices
emphasizing on the ability of parallelization and miniaturiza-
tion and the degree of automation.
Early, fast and accurate detection of a chemical and/or
biological material is critical to an effective response. Hence,
to achieve this goal, an integrated/hybrid sensor system is
highly desirable for broadening the benefits to the society.
Fig. 10 presents the schematic of conceptual hybrid platforms
of chemical and biological sensors based on NRs (left), NPs
(middle) and molecular-modified NPs film (right). Emphasiz-
ing on human health and clinical use point of view, the greatest
need is for the development of hybrid biosensors capable of
detecting collectively glucose, cholesterol, uric acid and other
clinically important biomolecules which can be easily operated
in laboratories or at home. Further, ‘wearable’ and ‘implan-
table’ biosensors along with supporting information techno-
logy network should be designed in order to overcome the
limitations of ambulatory technology and possible worsening
of the clinical situations of patients. In support of this vision,
one big concern is the sensor response time, accuracy, stability,
selectivity, and reproducibility. Some general strategies should
be developed to mitigate all these challenges by customizing
the sensing materials with numerous functionalities tailored to
specific physical properties and applications.
Another integrated conceptual sensor is a hybridized
chemical and biological sensor possessing the ability to sense
multiple toxic gases as well as hazardous biological substances
such as pathogenic microorganisms, bacteria, viruses, etc. This
ideal new sensor can be applied to various areas such as
hospitals, defence areas or war zones, pharmaceutical, pesti-
cide, textile and meat industries, houses, etc. Also, it will be
able to identify outbreaks of growing natural infectious dis-
eases or industrial accidents. Moreover, this sensor will help to
explore new opportunities to detect, identify and/or quantify
important biological and chemical features and processes in
the ocean. All these new and innovative technological
approaches will need to be more selective, sensitive, reliable,
fast responding, capable of autonomous screening, able to
convey securely and wirelessly in real- or near-real-time.
Fig. 10 Schematic of conceptual hybrid platforms of chemical and
biological sensors based on metal oxide nanostructures.
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10382 Chem. Commun., 2012, 48, 10369–10385 This journal is c The Royal Society of Chemistry 2012
Abbreviations
hIgG Human immunoglobulin G,
r-IgGs Rabbit-immunoglubin antibodies
BSA Bovine serum albumin
DPV Differential pulse voltammetry
CV Cyclic voltammetry
CEA Carcinoembryonic antigen
CPE Carbon paste electrode
PSA Prostate specific antigen
CILE Carbon ionic liquid electrode
MB Methylene blue
BMIMPF6 1-butyl- 3-methylimidazolium hexafluorophosphate
EIS Electrochemical impedance spectroscopy
PEPCase Phosphoenolpyruvate carboxylase
PNA Peptide nucleic acid
GOPS 3-glycidoxypropyltrimethoxysilane
ssCT-DNA Single standard calf thymus deoxyribose nucleic
acid
Acknowledgements
This work was supported in part by the Pioneer Research
program (2012-0001039) and by the World Class University
program (R31-20029) funded by the Ministry of Education,
Science and Technology through the National Research Foun-
dation of Korea.
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