2.3. Gas-sensing performance characterizations
With increasing temperature, our P-LIG sensor device shows a decrease in resistance (
Figure S4); its responses toward 1000 ppm of NO2 were examined to determine the optimal operating temperature. The relative response, ∆R/R
0 (%), of the sensor was calculated by equation (2):
where
Rg and
R0 are the sensor resistances under the analyte gas and under N
2, respectively.
Figure S1 shows comparison graphs for the response of the P-LIG sensor device to 1000 ppm NO
2 as the temperature was varied from 50°C to 150°C. The response shows an approximately twofold increase as the temperature was increased from 50°C to 100°C; however, once the response reached its maximum at 100°C, it decreased as the temperature was increased further to 150°C, where its value was even lower than that at 50°C. Because adsorption and desorption are temperature-sensitive processes, the deterioration in response at 150°C might be attributable to a decrease of the Debye length as the charge-carrier density increases at high temperatures and also to the untimely desorption of the adsorbed gas molecules bound to the graphene before an electrical interaction occurred between them.[
30,
31,
32] These factors might lead to a shift of the baseline resistance, thereby hindering the detection of a minute variation in resistance that occurs via gas adsorption or desorption. Therefore, the temperature of 100°C was selected as the optimal operating temperature for all of the gas-sensing tests.
After optimizing the operation temperature, we exposed the P-LIG sensor device to different gas concentrations ranging from 250 to 1500 ppm for both NO
2 and NH
3 to investigate the sensitivity of the LIG devices. The results in
Figure S5 show that the response saturation started from 500 ppm of NO
2, whereas no substantial variation in response was observed for elevated NH
3 concentrations. Because the highest responses were detected for 1000 ppm NO
2 and also 1000 ppm NH
3, the gas concentration of 1000 ppm was chosen for NO
2/NH
3 response tests to evaluate the influence of metal dopants on the LIG gas-sensing performance.
Figure 3 shows a set of seven single-response cycles for the P- and M-LIG sensor devices exposed to 1000 ppm NO
2 (a) and NH
3 (b) at 100°C while a DC bias of 1 V was applied. In fact, all of the tests were run with three on–off cycles and each cycle consisted of 10 min analyte-gas purging and 25 min N
2 purging for the "on" and "off" cycles, respectively (
Figures S6 and S7). When the devices were exposed to NO
2, a negative trend in ∆
R/
R0(%) was observed for all of the devices as the resistance decreased, whereas a positive tendency was observed as the resistance increased upon exposure to NH
3. This typical phenomenon can be observed when the graphene with a p-type conducting characteristic is in contact with an oxidizing agent (i.e., electron acceptor, NO
2) or reducing agent (i.e., electron donor, NH
3).[
10,
33,
34] In addition, graphene synthesized under ambient conditions typically exhibits p-type conduction, where the major carriers are holes, because of adsorbed oxygen or water molecules.[
35] Thus, as depicted in
Figure 4, once the p-type graphene is exposed to an oxidizing NO
2 gas, the hole accumulation within the graphene occurs after electron migration from graphene to the gas molecules, which results in a decrease in resistance. Meanwhile, upon contact of the sensors with a reducing NH
3 gas, electron injection from gas molecules into graphene reduces the major carrier concentration of the graphene; as a result, the overall resistance increases. In addition, we note that the sensitivity (
S,
) of both the P- and M-LIG sensor devices toward NO
2 gas is much higher than that toward NH
3 gas. As the first-principles study validated, this difference might be attributable to the higher adsorption energy (~67 meV) and charge transfer (~0.099e from graphene to a gas molecule) of NO
2 compared with those of NH
3 (~31 meV and ~0.027e for the adsorption energy and charge transfer from molecules to graphene, respectively) when they are adsorbed onto the surface of graphene.[
10,
36]
To investigate the role of metal incorporation into the LIG on the gas-sensing performance of LIG-based sensors, we selected metal dopants frequently used in first-principles studies of metal-doped graphene (i.e., Ag, Al, Au, Cu, In, and Pd) to fabricate the M-LIG sensor devices.[
11,
12,
13,
14,
16,
17,
36,
37,
38,
39,
40] As shown in
Figure 5, the NO
2 response of the P-LIG device was superior to those of all of the M-LIG devices. This deterioration in NO
2 response of the M-LIG sensor devices cannot be explained by a simple difference in work function between the metal NPs and LIG. (When work-function differences between pure metals and graphene are considered, the sensitivity should show a trend of high-work-function metal-doped LIG < LIG < low-work-function metal-doped LIG.) The deterioration is rather explained by considering the sophisticated interactions between the metal NPs and LIG, the metal NPs and NO
2, and the LIG and NO
2. To this end, an interpretation based on the electronic structures of metal NPs, LIG, and gaseous analytes can be applied to understand the inferior responses of the m-LIG sensor devices toward NO
2.
First, we focused on the oxidation of metals on the surface of LIG. According to the analyzed XPS data, the M-LIG sensor devices with highly oxidized surfaces (Al, Cu, and Pd) demonstrate weaker responses to NO
2 than the devices with metals with relatively weakly oxidized surfaces (Ag, Au, and In). In general, the oxidation of a metal dopant on a sensing layer can modify the surface properties and the overall electronic structure of the sensing material by changing the charge state.[
41,
42,
43] Moreover, the oxidized metal dopant can react with a vacancy in the host material (p-type) at a relatively high temperature (~100°C) to generate electrons via the electronic compensation mechanism. These electrons can contribute to a reduction of the hole carrier concentration through electron–hole recombination, negatively affecting the sensing performance of the p-type LIG.[
44,
45,
46] In addition, compared with the pure metallic catalysts on LIG, their undesirable oxidation might diminish the spill-over effect by shrinking its active reaction site for gas molecules and, consequently, decreasing the sensitivity[
47,
48] Among the highly oxidized metal-doped LIG devices, the NO
2 response is ranked in order of Al, Cu, and Pd and their work-function order is Pd > Cu > Al.[
12] The slightly stronger response of the Al-doped LIG device might originate from the formation of a hole-depletion zone in the LIG adjacent to the interface with Al NPs.[
49] Because the work function of Al is lower than that of multilayered graphene, a Schottky contact is generated by a large Fermi-level difference between the Al metal and p-type graphene, which leads to the formation of the hole-depletion zone in the LIG.[
12,
50] This hole depletion promotes electron charge transfer from the LIG to gas molecules (
Figure 6) and thus enhances the sensing response to NO
2.[
7] By contrast, the adsorption of the higher-work-function Cu onto LIG creates a hole accumulation zone at the interface via the p-doping effect on the LIG.[
49] This hole accumulation zone impedes electron charge transfer from the LIG to NO
2 molecules, thereby weakening the response to NO
2.
Oddly, the surface of the Pd-doped LIG is highly oxidized even though Pd is a noble metal; consequently, the Pd-doped LIG device exhibits the weakest response among the investigated devices. The Pd-doped LIG device exhibiting the weakest response to NO
2 among the investigated devices, in addition to being attributable to the weak surface oxidation of Pd, In addition to its highly oxidized surface, the weakest response of the Pd-doped LIG deivce towards NO
2 might also be attributable to Pd substantially damaging the conical points of graphene at
K via hybridization between the graphene
pz states and the Pd
d states, impeding the charge transfer of graphene.[
14] In the case of the relatively less-oxidized metals, the M-LIG devices show a response order of Ag, Au, and In toward NO
2. Although the work function of In is lower than that of Ag and Au, its corresponding response is inferior to the others and is even similar to that of highly oxidized metals.[
13] Chandni et al.[
39,
40] and Jia et al. investigated the transport of In adatoms on graphene and found that In adatoms drastically reduce the carrier mobility of the graphene and increase the level of charge-density inhomogeneity in the graphene, possibly resulting in a weaker response toward NO
2. In a comparison of the Ag- and Au-doped LIG devices, the Ag-LIG device exhibits a slightly stronger response because of the lower work function of Ag.[
12]
In contrast to the NO
2 response results, all of the investigated metals appear to have participated in the enhancement of the NH
3 gas response (
Figure 3(b) and
Figure 5). An approximately three- to four-fold increase in relative response was observed in the M-LIG sensor devices compared with the P-LIG device. As previously mentioned, NH
3 exhibits a lower adsorption energy and a lower charge transfer rate than NO
2; in this case, the chemical sensitization effect of metal NPs on LIG might play a dominant role in the sensing mechanism for NH
3 detection. In general, metal NPs on a sensing film tend to offer more active sensing sites for the analyte gas and to catalytically promote the dissociation of gas molecules into their more reactive status, leading to a sensitivity enhancement.[
51,
52,
53] Similar to the influence of metal oxidation on the NO
2 response, greater metal oxidation led to a lower NH
3 response; notably, however, reducing the charge carrier mobility by introducing In as a dopant might profoundly lower the sensitivity, resulting in the weakest response toward NH
3. Meanwhile, among the M-LIG sensor devices, the Ag-doped LIG device exhibited the strongest response to NH
3 as its ranked order in response toward NO
2.