In contrast to single-phase systems, different conduction paths are formed in binary two-phase systems by aggregates of component particles contacting with each other. Below we consider the influence of the nature and structure of conduction pathways, as well as the interaction between components, on the conductivity and sensor properties of nanocomposites. The mechanisms of chemical and electronic sensitization of sensor processes are also discussed.
2.2.1. Effect of conduction pathways on sensor properties of binary two-phase nanocomposites
The conductivity of the sensor layer is determined by the aggregates of metal oxide particles that are in contact with each other and form current flow paths. In a two-component system, in which components A and B form different crystalline phases, there are three types of intercrystalline contacts namely homophase contacts A-A and B-B, and heterophase contacts A-B. As a rule, nanoparticles A and B have different work functions (W) such that upon their contact, electron transfer occurs: at W
A > W
B from B to A, and at W
B > W
A, in the opposite direction. Such an electron transfer between nanoparticles corresponds to their mutual charging [
27].
Internal electric field develops at heterogeneous contacts. In this case, the potential barrier that prevents the passage of current through a heterogeneous contact between particles depends on the mutual direction of the internal and external fields [
72]. In a disordered system of nanoparticles, which includes heterogeneous contacts, when the direction of the external field is opposite to the direction of the field in the contact, high barriers inevitably arise on the current path. The current flow path “bypasses” such contacts, choosing for electron transfer the homogeneous contacts with lower barriers [
72].
Thus, in two-phase nanocomposites consisting of particles of components A and B, two parallel homophase conduction paths can be realized through the contacting nanoparticles A-A or B-B. The current flows through chains of contacting nanoparticles, which form conducting clusters that connect the electrodes of the measuring system (“endless” clusters [
72,
73]). The nanoparticles of the second component that did not enter the conduction pathways are modifiers, the interaction with which changes the chemical and electronic characteristics of the conducting nanocrystals, and, consequently, the conductivity and sensor effects.
In a disordered two-phase conglomerate from particles of two components, the conduction paths are determined by the percolation theory [
73] and depend on the relative content of the components and the ratio between the sizes of the corresponding nanocrystals [
72].
In nanostructured composites ranging from
n- and
p-modifications of TiO
2, three conduction regions are possible [
72] based on the percolation model, depending on the relative content of the components. These are regions I and II with conducting clusters of nanoparticles of only one type, and region III, in which conducting clusters of both types coexist. In region III, the conductivity of the composite depends on the ratio between the concentrations of components, the size of the particles, and the concentration of current carriers (electrons or holes) in the components [
72].
In a nanostructured composite of metal oxides with different work functions, the magnitude and direction of the sensor effect are determined by the electron transfer between the conducting clusters and the modifier. A characteristic example is the result obtained from the study of the conductivity and sensor effect in a composite of SnO
2 nanofibers with nanoclusters of TiO
2 or WO
3 modifiers located on the surface of the nanofibers [
74]. In SnO
2 nanofibers and modifier nanoclusters, the work function is different; therefore, the effect of modifiers on conductivity and sensor properties depends on the difference between W
SnO2 and W of the modifier. Modification of nanofibers with TiO
2 nanoclusters (W
TiO2 < W
SnO2) leads to an increase in the conductivity of the composite due to electron transfer from TiO
2 to SnO
2, while modification with WO
3 nanoclusters (W
WO3 > W
SnO2) reduces the conductivity due to electron transfer from SnO
2 to WO
3 [
74].
The modification of SnO
2 nanofibers also changes sensor effects in addition to the conductivity. An increase in conductivity under the influence of TiO
2 causes an increase in the sensor effect for oxidizing gases but has almost no effect on the sensor effect for reducing agents. The decrease in conductivity caused by WO
3 nanoclusters also leads to an increase in the sensor effect in the detection of reducing gases [
74].
A similar increase in the sensor response to reducing gases, accompanied by a decrease in the conductivity of the composite, is observed for the deposition of WO
3 nanoclusters on the surface of In
2O
3 nanofibers. In contrast, the deposition of In
2O
3 on WO
3 nanofibers increases their conductivity and sensor response to oxidizing gases, but reduces the sensitivity of the composite to reducing agents [
75].
In numerous reviews on two-phase nanocomposites (see, for example, [
76,
77]), as in the studies considered above, only systems with conduction paths from particles of one component are mostly discussed. Particles of the second component interacting with conductive particles change their properties and affect sensor effects.
Binary nanocomposites with different conduction paths have different sensitivity to detected gases. The authors of [
78,
79] studied systems consisting of metal or metal oxide nanoparticles in combination with thin nanolayers of reduced graphene oxide (rGO). At small coverage of rGO layers by Pd particles these layers are current flow paths, and the conductivity decreases in the presence of hydrogen. This is due to the transformation of Pd nanoparticles into PdH
x, followed by electron transfer from PdH
x to rGO and a decrease in the concentration of charge carriers – holes – in the
p-semiconductor rGO [
78].
With an increase in the concentration of Pd particles, the response to H
2 decreases due to a change in the conduction paths – from rGO layers to clusters of Pd nanoparticles. This occurs during the formation of a continuous Pd film on the surface of the rGO layers. Due to the change in the structure of the Pd film under the influence of hydrogen dissolved in it, the response increases [
78]. In the absence of Pd nanoparticles the conductivity of rGO layers largely does not react to the presence of nonpolar molecules in the air, for example, H
2. The effect of current flow paths in nanocomposites combining rGO layers with metal oxide nanoparticles on conductivity and sensor properties was studied in detail using the response to ammonia as an example [
80].
As rGO was added to nanostructured SnO2, the type of conductivity of the composite changed from electronic conductivity, characteristic of pure SnO2, to hole conductivity, characteristic of rGO. Due to the difference in the shape of the components (thin extended rGO nanolayers and quasi-spherical SnO2 nanoparticles), the percolation transition from n- to p-composites occurs already at small (about 0.5 wt.%) additions of rGO to SnO2.
These experimental results agree with the calculations [
80]. The response of the sensor to ammonia is due to its reaction with oxygen anions on the surface of SnO
2 particles. In n-type nanocomposites where the current flows through clusters of SnO
2 nanoparticles, the addition of ~0.5 wt.% rGO leads to an increase in the electronic conductivity of the composite [
80]. Since W
rGO (5.2 eV) of a completely reduced graphene oxide film [
81] is larger than W
SnO2 (4.9 eV), electrons pass from SnO
2 to rGO. As a result, the electron concentration in conducting clusters of SnO
2 nanoparticles decreases, which increases the response to reducing gases [
74,
82].
In connection with the mutual charging of contacting SnO
2 nanoparticles and rGO nanolayers, during the transition of electrons from SnO
2 to rGO, favorable conditions are created for the adsorption of polar molecules in the contact region in the nanocomposite. This also applies to NH
3 molecules and additionally increases the sensitivity of the composite sensor to ammonia. An increase in rGO concentration to 1 wt.% leads to a percolation transition from conduction through SnO
2 particles to conduction paths through rGO layers, that is, to hole conduction [
80].
The paths of hole and electron conduction are different in nanostructured metal oxides, [
77,
83]. The electron current flows through contacting nanoparticles, crossing their surface layers where potential barriers are formed between the particles due to oxygen ionosorption accompanied by the capture of electrons from the conduction band. The resistance of the surface layers is significantly increased compared to the resistance in the bulk of the particles. The height of such barriers on the current path is determined by the number of electrons captured by oxygen, which decreases when O
– interacts with a reducing gas. This leads to an increase in conductivity.
In the case of hole conduction, the current flows mainly in the near-surface layers of
p-nanoparticles. Wherein, the negative charge of O
- on the surface is compensated by the positive charge of holes in the near-surface layer. The concentration of holes in this layer is naturally higher than in the volume of the particles [
83,
84]. The total resistance to hole current in the volume of the particles and surface layers is determined by the morphology of the nanostructured metal oxide [
85].
At the hole conduction, the total resistance R
sen of the sensor layer includes a volume component which is largely independent of the processes on the particle surface. Therefore, the sensitivity to reducing gases in such systems is significantly less than in the case of electronic conduction, when the change in resistance is determined by the reactions of the analyzed gases with O
- on the surface of the particles. SnO
2-rGO sensors to ammonia with hole conduction along the paths formed by rGO layers are characterized by greater stability and shorter response time to ammonia and relaxation time after its removal [
80].
The conductivity and sensor properties of nanocomposite fibers containing
n-SnO
2 and
p-Co
3O
4 nanoparticles were studied in [
23]. The resistance of the
xSnO
2 – (1-
x)Co
3O
4 system and its sensor response to CO, C
6H
6, and С
3H
6O reach their maximum values at
x = 0.5. A nanofiber of this composition has electronic conductivity. Since the arrangement of nanoparticles in a fiber is chaotic, the conductivity of a nanocomposite fiber is determined by the percolation model [
72,
73].
According to this model, the electron current in such a system flows along
n-type homophase paths, excluding heterophase
n-
p contacts, the inclusion of which in the current path would lead to the occurrence of large potential barriers. Heterophase contacts between
n- and
p-nanoparticles of composite lead to the loss of electrons due to electron-hole recombination. As a result, the electron concentration in the conducting channels decreases. This in some cases leads to an increase in the response to reducing gases [
83].
Similar effects are also characteristic of other
n-
p nanocomposites [
86,
87], in which the maximum response is achieved in the systems with electronic conductivity. The sensitization of sensor response by
p-nanoparticles contacting with
n-nanoparticles of conducting pathways is due to a decrease in the electron concentration in conducting pathways resulting from electron-hole recombination. At
n-n-contacts, the concentration of conduction electrons does not decrease, but the electrons pass into a lower-energy conductivity band, forming an “accumulation layer” of electrons in acceptor centers [
83,
88]. Such a transition also reduces the concentration of conduction electrons in the conducting paths of the composite, but to a lesser extent since the transition of electrons is hindered by the resulting electric field. Therefore,
n-p contacts are more effective for sensitizing the composites having the electronic conductivity.
2.2.2. Effect of interaction between conducting and modifying nanocrystals on sensor properties of a composite
In binary systems, the interaction of nanoparticles constituting current flow paths with modifier nanoparticles surrounding these paths is a source of sensor sensitization. There are two types of sensitization: chemical and electronic [
13,
89].
Chemical sensitization is caused by catalytically active particles of the modifier, which chemisorb oxygen and molecules of detected gases with the formation of reactive particles, in particular, atoms or radicals. The most common variant of chemical sensitization is the adsorption and dissociation of oxygen molecules on modifier particles with subsequent spillover of oxygen atoms into conducting clusters. After that, oxygen atoms capture electrons from the conduction band of nanoparticles constituting conducting clusters, forming O- radical anions.
Since the reaction of reducing gases with O
- on the surface of conducting clusters “releases” trapped electrons and increases the conductivity of the composite, the concentration of adsorbed oxygen should be increased to increase the sensitivity. Cleary, this is facilitated by the catalytic activity of modifier nanoparticles [
14,
90].
The detection of several π-electron compounds by sensors based on SnO
2 nanofibers modified with Au, Pd, and Pt nanocrystalline particles was studied to determine the optimal conditions for achieving the maximum sensitivity [
91]. The study indicated that the adsorption bonds of π-electron molecules with metal particles are determined by the location of the metal d-electron band relative to the π-electron orbitals of the molecules of the analyzed gases. Therefore, by varying the electronic structure of the contact between a gas molecule and a metal particle on the surface of SnO
2 nanofibers, chemisorption can be increased. The spillover of adsorbed molecules from metal particles onto SnO
2 fibers increases the gas concentration on nanofibers and the sensitivity of the composite. The conditions were determined for the most efficient chemical sensitization of the sensor effect by Au, Pd, and Pt particles in the detection of CO, benzene, and toluene [
91].
Chemical sensitization depends both on the structure of the detected molecule and the properties of the catalytically active particle. A typical example is the sensitization of CO and H
2 detection by a sensor based on nanocrystalline In
2O
3 containing nanoparticles of the well-known catalyst, ZrO
2. The particles of ZrO
2 increase the sensor effects in the detection of H
2, but practically do not affect the detection of CO [
92].
The effect of chemical sensitization of the sensor response to CO in this system could be expected due to the dissociation of O
2 on the surface of ZrO
2 nanoparticles with the subsequent formation of O
- active centers. However, the dissociation of O
2 requires a temperature above 800 °C [
93]. The efficiency of H
2 detection is probably ensured by the dissociation of H
2 molecules under the influence of ZrO
2. As a result of the spillover of the formed hydrogen atoms onto In
2O
3 particles, H atoms react with O
- radical anions localized on the In
2O
3. In this case, the electrons captured by oxygen return to In
2O
3.
The conductivity of a nanofiber network is determined by potential barriers to electron transfer between contacting nanofibers and depends on the electron concentration in their surface layers (
ns) [
83]. The decoration of SnO
2 fibers with electron-donating TiO
2 (W
TiO2 < W
SnO2) or electron-withdrawing WO
3 (W
WO3 > W
SnO2) nanoclusters leads to a redistribution of conduction electrons between conducting channels and decorating clusters [
74]. The transfer of electrons from SnO
2 nanofibers to WO
3 nanoclusters reduces
ns and increases the barriers for electron transfer between contacting nanofibers [
83]. All this affects the sensor effect [
68] and can be considered as electronic sensitization.
The sensor properties of nanocomposites depend on the method of their formation, which determines their morphology. In this regard, the indicators are the results of studies of composites obtained by physical mixing of oxide nanopowders or by laser sputtering of one oxide on the surface of crystals of another [
21,
22,
94,
95,
96]. In such composites based on electron acceptor SnO
2 or ZnO oxides, electron-donating additives of In
2O
3 or TiO
2 nanoparticles do not decrease the sensor effect for reducing gases, as in [
74,
97,
98], but increase it.
It should be noted that the sensor characteristics of binary composites obtained by mixing nanocrystalline powders, in contrast to the systems considered in [
74,
97,
98], are mainly determined by the contacts of particles with different electron affinities and clearly marked interphase boundaries [
94], where the charges formed as a result of mutual charging of such particles are localized. Charges in the interfacial regions of the nanocomposite, as mentioned above [
80], can increase the chemisorption of oxygen and detected gases and, thus, increase the sensor effect.
The effect of interfacial contacts on the sensor properties of nanocomposites was not considered in [
74,
75]. This is probably due to the small size of electron-donor and electron-acceptor clusters located on the surface of conducting nanofibers, because of which the distribution of electrons in the region of these contacts is largely blurred.
It can be assumed that the differences in the sensor properties of nanocomposites obtained by different methods are due to the structure of the interfacial regions in such composites, which determines the adsorption of gases and their activity in sensor reactions. The largest increase in the sensor effect is achieved due to the joint effect of chemical and electronic sensitization by chemically active modifiers with a high work function [
90].
Such sensitization of the sensor effect occurs, in particular, due to the modification of the surface of conducting metal oxide particles by nanoclusters of catalytically active metals Au, Pd, and Pt [
91]. Nanoclusters of these metals, as shown above, catalyze the formation of highly reactive atoms and radicals on the surface of metal oxide nanocrystals, which corresponds to chemical sensitization. These nanoclusters, which have a higher work function than conductive metal oxide nanocrystals, capture the electrons of the nanocrystals, lowering
ns. Thus, there is also an electronic sensitization of the sensor effect.
A characteristic example of the synergism of electronic and chemical sensitization is the detection of ethanol vapor by sensors based on In
2O
3 nanotubes decorated by nanoclusters Co
3O
4, Fe
2O
3 or a combination of these nanoclusters [
99]. The deposition of nanoclusters of even a single metal oxide on the surface of nanotubes increases the sensor effect due to electron sensitization since the work function of these metal oxides is higher than that of In
2O
3. In this case, Co
3O
4 clusters have a greater influence, although W for Fe
2O
3 (5.3 eV [
100]) is higher than for Co
3O
4 (4.8 eV [
101]).
Co
3O
4 nanoclusters are both electronic and chemical sensitizers, which is due to the catalytic activity of Co
3O
4 in the dissociation reactions of adsorbed oxygen molecules with the formation of O
-. The largest increase in the sensor effect occurs with the joint application of Co
3O
4 and Fe
2O
3 when high chemical sensitization of the sensor effect under the action of Co
3O
4 is combined with high electronic sensitization under the influence of Fe
2O
3 [
99].
The synergism of the sensitizing action of different agents is also manifested in sensors based on porous In
2O
3 nanospheres modified with NiO and Au nanoclusters [
102]. The interaction of NiO clusters with In
2O
3 leads to the formation of oxygen vacancies on the surface of In
2O
3 in such systems due to the difference in the charges of Ni
+2 and In
+3 ions. Concurrently, Au nanoclusters catalyze the dissociation of these molecules, with the capture of electrons and the formation of O
- active centers.
The combined action of NiO and Au clusters on In
2O
3 nanoparticles produces high sensitivity in the detection of reducing compounds, in particular, toluene [
102]. Using such a sensor, toluene can be detected even at concentrations on the order of 100 ppb, since Au clusters adsorb toluene and thus increase the sensor effect. A similar synergistic effect of electronic and chemical sensitization of the sensor effect was also found for In
2O
3 nanotubes containing NiO and PdO nanoclusters on the surface [
39].
The results presented in this Section have shown that the sensor response for two-component two-phase metal oxide composites can differ markedly for various gases.
Table 1 summarizes the results of previous investigations, and makes it possible to compare the response magnitudes to various gases of sensors synthesized with different methods under diverse conditions.
The consideration of the processes of chemical and electronic sensitization of sensor reactions has shown that such a division is rather arbitrary. For example, oxygen molecules dissociate on the surface of nanoparticles with the formation of chemically active centers, which corresponds to chemical sensitization. Wherein, the formed oxygen atoms actively capture electrons from the near-surface layer, depleting it: this is already characteristic of electron sensitization. Thus, in various sensor processes, both types of sensitization mechanisms can occur simultaneously, but the chemical or electronic nature will be manifested to a greater extent.