Ian J.
Echols
a,
Hyosung
An
a,
Xiaofei
Zhao
a,
Evan M.
Prehn
b,
Zeyi
Tan
b,
Miladin
Radovic
*b,
Micah J.
Green
*ab and
Jodie L.
Lutkenhaus
*ab
aArtie McFerrin Department of Chemical Engineering, Texas A&M University, College Station, TX, USA. E-mail: Jodie.lutkenhaus@tamu.edu; Micah.green@tamu.edu
bDepartment of Materials Science and Engineering, Texas A&M University, College Station, TX, USA. E-mail: Mradovic@tamu.edu
First published on 11th December 2019
The importance and widespread need for accurate pH monitoring necessitates the fabrication of new pH sensors with high sensitivity that can be used in a variety of environments. However, typical pH sensors have certain limitations (e.g., glass electrodes are fragile and require consistent upkeep, colorimetric pH strips are single use and inaccurate). Herein, we examine the pH-response of multilayers consisting of Ti3C2Tx nanosheets and polycations fabricated using layer-by-layer (LbL) assembly. The MXene sheets themselves are pH-responsive due to their hydroxyl surface groups, and this effect may be amplified with the choice of an appropriate polycation. Specifically, the performance of multilayers assembled with the strong electrolyte poly (diallyldimethylammonium) (PDADMA) or pH-sensitive branched polyethylenimine (BPEI) is compared. As expected, the use of a pH-sensitive constituent leads to a 464% increase in pH sensitivity (116 kΩ pH−1 unit vs. 25 kΩ pH−1 unit) as compared to PDADMA. This is due to the conformational changes that BPEI undergoes with (de)protonation as pH changes. Further comparisons with reduced graphene oxide (rGO), which is far less pH responsive, confirm the unique pH responsivity of MXene nanosheets themselves. The ability to enhance response to particular stimuli by changing the constituent polycation demonstrates promise for future use of MXenes in resistive sensors for a variety of stimuli.
Design, System, ApplicationMXenes, a family of two-dimensional metal carbides, have drawn increasing interest for use as sensors due to their metal-like conductivity and surface functional groups. In this work, we employed layer-by-layer (LbL) assembly to fabricate uniform polycation/MXene thin films with different polycations. We then exposed the fabricated films to environments of varying pH to determine the usable range and pH response of the films. This resulted in a pH range limited by the oxidative stability of the MXenes and a linear increase in resistance with pH over the usable range. By comparing thin films assembled with either a pH-insensitive or a pH-sensitive polycation, we were able to determine both the pH sensitivity of the MXene itself and the benefits of a pH-sensitive polycation. These results were further compared to similar films containing reduced graphene oxide instead of MXenes. This work demonstrates the ability to enhance sensitivity of MXene based films by using a pH sensitive polycation and generates promise for tailoring future LbL polycation/MXene sensors to specific analytes such as VOC's and biomolecules. |
An alternative approach explored herein is resistive sensors. This sensor type relies on a change in electrical properties in response to environmental stimuli. As such, materials used in the fabrication of resistive sensors are ideally highly conductive and have functional surface groups that can interact with the surrounding environment. One such material that satisfies both requirements is Ti3C2Tx, a 2D-nanomaterial in the MXene family. As the most commonly used MXene to date, Ti3C2Tx nanosheets have demonstrated a conductivity of 240000 S m−1 and have numerous hydroxyl surface groups.16,17
MXenes with the chemical formula Mn+1XnTz are obtained by the selective etching of the ‘A’ element from a MAX phase material, in which A is a group 13 or 14 transition metal, M is a transition metal, X is either carbon or nitrogen, T is a surface terminal group (e.g., –OH, –O, and –F), and n is 1, 2, or 3.18–20 MXenes have been used for a variety of applications including energy storage, catalysis, membrane separation, and sensing.21–34 These applications are possible due to the intercalation of ions between the 2D nanosheets, high conductivity, abundance of hydroxyl sites, and high surface to volume ratio.21,35–38
However, a major drawback of MXenes is their proclivity to oxidation when exposed to water.39–42 Oxidation of Ti3C2Tx to TiO2 leads to noticeable degradation in conductivity, flocculation of the colloidal dispersion, and -ultimately- complete conversion to TiO2.39,40 This greatly impedes the shelf life of MXenes and their longevity in devices. Our team has demonstrated that anti-oxidants (e.g., sodium L-ascorbate (NaAsc)) mitigate the effects of oxidation for Ti3C2Tx.43 Adding an antioxidant enables the retention of Ti3C2Tx conductivity in MXene films for at least three weeks.43 This considerable increase in shelf life enables the use of MXenes in different applications. The new-found stability motivates us to investigate the resistive pH-response of Ti3C2Tx nanosheets when assembled with various polycations into thin films.
The colloidal pH-response of MXenes in a dispersion has been explored, but the changes in electrical properties in response to pH have not been explored in depth.3,44–46 For example, Natu et al. reported on the acid- and base-induced crumpling of Ti3C2Tx.44,45 Natu et al. also demonstrated a pH dependence of both zeta potential and hydrodynamic size for Ti3C2Tx.44 This is attributed to the (de)protonation of the hydroxyl surface groups of the MXene and creates promise for use of Ti3C2Tx for pH sensing. Recently, drop-cast Ti3C2Tx films and quantum dots have successfully been used to fabricate potentiometric and photoluminescent pH sensors, supporting the pH sensitivity of Ti3C2Tx.3,46
Here, we explore the layer-by-layer (LbL) assembly of Ti3C2Tx nanosheets with two different polycations and observe the resistive response of the resulting multilayers to aqueous solutions of various pH values. LbL assembly is selected as the processing method because it forms conformal coatings that have already demonstrated utility as strain and humidity sensors.25,26 This potentially allows for the fabrication of thin films on a variety of substrates including glass, polyethylene terephthalate (PET), polydimethylsiloxane (PDMS), fibers, and fabrics, regardless of topography.26 Cai et al. recently showed the benefits of LbL assembly over direct mixing when fabricating thin films, in which ordered structures obtained using LbL assembly prevented restacking of MXene nanosheets and improved recoverability of the sensors.24
Two polycations are explored in this work: poly(diallyldimethylammonium) (PDADMA) and branched polyethylenimine (BPEI). As PDADMA is a “strong” electrolyte, its linear charge density does not fluctuate with pH.47 Therefore, it is assumed that the resulting resistive response of PDADMA/Ti3C2Tx assemblies is attributed solely to the MXene itself. We compare this to sensors containing BPEI, which is considered a pH-sensitive “weak” polyelectrolyte,15 instead of PDADMA. As demonstrated for polyaniline-based pH sensors, we expect that BPEI will contribute to pH sensitivity due to (de)protonation of its amine groups.48 BPEI bears three amine groups, which each have unique pKa values (4.5 for primary amine, 6.7 for secondary amine, and 11.6 for tertiary amine). In LbL assemblies (all-polymer, no MXenes), varying pH leads to conformational changes for BPEI, resulting in changes in the thin film thickness.49–51 This is due to chain elongation of BPEI at low pH, resulting in minimal contribution of the polymer to film thickness. The opposite occurs at high pH. For BPEI/Ti3C2Tx assemblies, we hypothesized that pH would influence both the MXenes (by changing the MXene surface chemistry) and the BPEI layers (by changing the chain conformation), manifesting in compounded changes in resistance. Finally, the results are compared to LbL assemblies containing reduced graphene oxide (rGO) in place of the MXene as a control. As rGO has fewer hydroxyl functional groups as compared to Ti3C2Tx MXene, rGO is expected to have negligible influence on pH sensitivity. Ideally, comparing PDADMA/Ti3C2Tx and PDADMA/rGO assemblies will highlight the pH sensitivity of the MXene. On the other hand, comparing PDADMA/Ti3C2Tx and BPEI/Ti3C2Tx assemblies will demonstrate the added pH sensitivity of BPEI as compared to PDADMA.
A batch of 0.5 mg mL−1 GO dispersion was synthesized following previous reports and the modified Hummers' method, see ESI.†53,54 This method resulted in nanosheets with a lateral size of 0.3 to 0.7 μm and a sheet thickness of 0.9 nm (Fig. S1b and d†). While the nanosheet thicknesses of both nanomaterials were similar, there was visible aggregation of the GO nanosheets.
Due to the hydrophilic nature and ease of processability of graphene oxide (GO), rGO-based multilayers were prepared by the chemical reduction of GO-based multilayers.54 HI vapor was used to reduce GO-based multilayers following a previously reported procedure.54 1 mL of 55% HI (aq.) was added to a glass petri dish along with the GO-based multilayer. The petri dish was covered with a secondary petri dish to prevent loss of HI vapor and then heated for 8 minutes at 90 °C. The reduced film was washed with ethanol and made into sensors as described previously.
Ti3C2Tx-only films were prepared by spray-coating onto PET substrates, combining the procedures of Zhao et al. and De et al.54,55 A 0.5 mg mL−1 dispersion of Ti3C2Tx was sprayed onto the substrate while maintaining a vertical distance of 15 cm and nozzle pressure of 80 psi. This continued for 8 minutes with constant movement (1 cm s−1) over the substrate. The spray-coated substrate was then fabricated into sensors.
Growth profiles were obtained for all multilayers fabricated. Measurements for GO multilayers were taken prior to reduction. Film thickness and root mean square (RMS) roughness (Rq) were measured using profilometry (KLA Tencor D-100) for LbL films on glass substrates. Thickness was verified using ellipsometry (LSE Stokes Ellipsometer) for LbL films on Si substrates. Absorbance was measured using spectrophotometry (Shimadzu SolidSpec-3700 UV-vis-NIR) of LbL films on glass. A quartz crystal microbalance (QCM, MAXTEK RQCM Research) was used to measure film composition from coatings on 5 MHz Ti/Au quartz crystal substrates. Frequency was measured after every deposition, and mass deposited was calculated from the change in frequency using the Sauerbrey equation.56
All measurements were taken at room temperature.
(1) |
(2) |
Fig. 2 (a) XRD of Ti3C2Tx nanosheets and Ti3AlC2 MAX phase. (b) SEM image of Ti3C2Tx nanosheets. Digital images of colloidal solutions of (c) Ti3C2Tx and (d) GO demonstrating the Tyndall effect. |
XPS verified the composition of the Ti3C2Tx MXenes. A survey scan (Fig. S3†) indicated the presence of the expected Ti 2p, C 1s, O 1s, and F 1s peaks associated with Ti3C2Tx. Peak fitting for each of these components is shown in Fig. S4,† and binding energy, atomic percent (at%), and full width half maximum (FWHM) are summarized in Table S1.† For Ti 2p, the Ti2+ (456.1 eV, 461.5 eV) and Ti3+ (457.9 eV, 463 eV) components correspond to the functional surface groups of the MXene (–OH, –O, and –F).43,59 The peaks at 455.2 and 460.3 eV correspond to Ti–C. Together, these peaks indicate the successful etching of the MAX phase into Ti3C2Tx. The C–OH peak (288.0 eV) of the C 1s spectra is present due to the interaction of NaAsc with the nanosheets, indicating the presence of NaAsc.43 The TiO2 peak (529.7 eV) of the O 1s spectra occurs due to the oxidation of Ti3C2Tx. The degree of oxidation is limited (11 at% of the Ti 2p spectra) and verifies the anti-oxidant properties of NaAsc, consistent with our previous findings.43 The amount of oxidation of the native Ti3C2Tx MXene will vary depending on storage time and conditions.
The linear growth was verified using ellipsometry on silicon substrates (Fig. S5a†). Despite lower growth rates as compared to profilometry measurements (3.1 nm per LP from ellipsometry vs. 8.8 nm per LP from profilometry in the case of (PDADMA/Ti3C2Tx)y multilayers), the linear growth profile of the films was confirmed. The difference in the magnitude of layer growth can be attributed to the indirect measurement method of ellipsometry and the interference of the MXene with the polarized light source.
Linear growth was additionally verified using spectrophotometry on coated glass substrates (Fig. 3c and S6a and b†). Digital images of the multilayers are shown in Fig. 3d and e. The absorbance of note was taken at 770 nm following previous reports.25 Absorbance of the films at 770 nm grew as 0.04 a.u. per LP for (PDADMA/Ti3C2Tx)y films and 0.01 a.u. per LP for (BPEI/Ti3C2Tx)y films. Subsequently, the linear increase in absorbance was then correlated with the thickness to create an empirical relationship between the two. This enabled later thickness measurements for substrates on which profilometry was not possible (e.g., PET substrates). QCM measurements on the Ti/Au quartz crystal were used to determine the mass composition of the polycation/Ti3C2Tx multilayers (Fig. S5c†). From this, a mass composition of 5.5% PDADMA and 94.5% Ti3C2Tx was calculated for (PDADMA/Ti3C2Tx)y multilayers. (BPEI/Ti3C2Tx)y multilayers were determined to consist of 9.3 wt% BPEI and 90.7 wt% Ti3C2Tx. In both cases, Ti3C2Tx dominates the growth of the film, verifying the assumption that layer growth can be primarily attributed to the MXene sheets.
To determine the viable range for pH response testing, a wide pH range (3–10) was first examined (Fig. S7a†). There was a drastic increase in resistance as the Ti3C2Tx multilayers were exposed to basic conditions. The increase is attributed to the rapid oxidation of Ti3C2Tx, which resulted in a noticeable color change upon exposure to basic conditions (pH ∼10) for 24 hours (Fig. S7c†). While this may seem an extended period, all films were exposed to a neutral environment (Milli-Q water) for 24 hours prior to testing to allow for swelling of the multilayers and did not undergo any notable color change. Given the increased rate of oxidation in basic environments, the pH range tested was restricted to pH 3 to pH 7.
Sensor performance was quantified by the pH sensitivity. A representative (PDADMA/Ti3C2Tx)5 sensor was tested first to determine the contribution of Ti3C2Tx to the pH response (Fig. 4a). The initial resistance of the film when exposed to pH 3 was 118 kΩ. As pH increased from 3 to 7, the resistance increased as 23 kΩ pH−1 (19.4 % pH−1). When decreasing pH back to pH 3, there was slight hysteresis – a typical observation for resistive sensors.7 Due to the hysteresis, the cycles were split based on whether pH was increasing or decreasing to determine repeatability (e.g., pH 3 → pH 7 and pH 7 → pH 3). While the sensitivity increases to 28 kΩ pH−1 by the third cycle, there is good overlap in response for pH 3 → pH 7 in Cycles 1 and 3. Using a 95% confidence interval, the sensitivity of the film was determined to be 24.8 ± 2.6 kΩ pH−1. Profilometric thickness was measured before and after pH response tests to determine recoverability of thickness. Thickness changed from 40.6 ± 10.9 nm to 43.7 ± 9.6 nm, suggesting the reversibility of the response.
Fig. 4 pH Response of (a) (PDADMA/Ti3C2Tx)5 and (b) (BPEI/Ti3C2Tx)5 sensors. The pH sensitivity was 24.8 ± 2.6 kΩ pH−1 for (a). The pH sensitivity was 115.7 ± 20.8 kΩ pH−1 for (b). |
A representative (BPEI/Ti3C2Tx)5 sensor was then examined to determine if a pH sensitive polycation would enhance sensitivity. The initial resistance of this film at pH 3 was 194 kΩ. The higher value of initial resistance as compared to (PDADMA/Ti3C2Tx)5 sensors is likely due to differences in thicknesses of the two films. Resistance is inversely proportional to thickness. As with the previous sensors, there was noticeable hysteresis when comparing response curves for increasing and decreasing pH. In this case, the initial pH sensitivity pH 3 → 7 was 132 kΩ pH−1 (68.1% pH−1), increasing to 141 kΩ pH−1 by the third cycle. This pH sensitivity is five times higher as compared to that of (PDADMA/Ti3C2Tx)5 sensors due to the further thickness changes caused by conformational changes of BPEI with pH. Additionally, the overlap for pH 3 → pH 7 in Cycles 1 and 3 is comparable to that for (PDADMA/Ti3C2Tx)5. This indicates cyclability of the sensors up to three cycles in both cases. Using a 95% confidence interval, the sensitivity of the film was determined to be 115.7 ± 20.8 kΩ pH−1. As with the previous sensor composition, profilometric thickness was measured before and after pH response testing. In this case, thickness changed from 22.7 ± 8.8 nm to 20.3 ± 2.9 nm, which indicates the reversibility of the response.
Given the proclivity of Ti3C2Tx to oxidize, SEM and XPS were used to characterize the sensors before and after pH response testing to determine the extent of oxidation. Oxidation of the films was first demonstrated using SEM as there was noticeable TiO2 on the surface of the sensors after pH response testing (Fig. 5c and d) that was not present on as-prepared sensors (Fig. 5a and b).
Fig. 5 SEM images of (a and c) (PDADMA/Ti3C2Tx)5 and (b and d) (BPEI/Ti3C2Tx)5 films before (a and b) and after (c and d) pH response tests. The scale bar in (a) applies to the other panels as well. |
XPS survey scans (Fig. S8†) confirmed the presence of Ti 2p, C 1s, O 1s, and F 1s before and after pH response tests. Formation of TiO2 was verified by peak fitting of the Ti 2p XPS spectra for both sensors before and after testing (Fig. 6). For both sensor compositions, there is a notable peak that forms at 458.7 eV, which is indicative of considerable oxidation (∼1% to ∼50% TiO2 component at% of the Ti 2p spectra). Deconvolution of the other components (Fig. S9 and S10†) supports the claim that oxidation occurred. For C 1s, there is a notable decrease in the C–Ti–Tx component peaks. For F 1s, the C–Ti–Fx peak becomes noticeably smaller and much closer in area to the AlFx peak. All XPS peak fitting results for the sensors are presented in Tables S2–S5† along with the full width half maximums (FWHM) and component at%. This oxidation likely contributed to resistance drift in the sensors from cycle to cycle.
Fig. 6 Deconvoluted Ti 2p XPS spectra of (a and c) (PDADMA/Ti3C2Tx)5 and (b and d) (BPEI/Ti3C2Tx)5 before (a and b) and after (c and d) pH response tests. |
The response for (PDADMA/Ti3C2Tx)5 sensors is attributed to (de)protonation of the hydroxyl surface groups of Ti3C2Tx. Due to changes in the net surface charge of the Ti3C2Tx nanosheets and the changes in the degree of protonation of the hydroxyl surface groups, the magnitude of electrostatic attraction/repulsion and the available number of charge carrier sites will vary, causing the observed changes in resistance. This mechanism is similar to that of graphene where H3O+ and OH− adsorb to surface sites.7 Recently, Natu et al. showed a linear decrease in zeta potential with pH over the pH range 2 to 7.44 The linear change in zeta potential supports the moderately linear pH response we observed and is in line with the proposed mechanism.
The increase in sensitivity for (BPEI/Ti3C2Tx)5 sensors is attributed to BPEI conformational changes with pH. Unlike PDADMA, BPEI is highly pH sensitive. As the exposure pH increases above the pKa values of BPEI, the degree of protonation of the amine groups will decrease, leading to decreased electrostatic repulsion. In sum, this results in a more coil-like conformation for BPEI chains at more basic pH values.60 We speculate that this will cause the distance between nanosheets to increase, causing the observed increase in resistance.25 This compounds with the resistance changes incurred by the Ti3C2Tx nanosheets, leading to the enhanced sensitivity.
The performance of sensors assembled with Ti3C2Tx without the treatment of NaAsc was evaluated to determine the effect of the added antioxidant (Fig. S11†). The pH responsivity for the first cycle was 72 kΩ pH−1 for (PDADMA/Ti3C2Tx)5 and 120 kΩ pH−1 for (BPEI/Ti3C2Tx)5 when Ti3C2Tx was not treated with NaAsc. While the pH sensitivity of the untreated (PDADMA/Ti3C2Tx)5 sensor was higher than that of the treated (PDADMA/Ti3C2Tx)5 sensor, the initial resistance was significantly higher (almost double) and the cyclability from pH 3 → pH 7 for cycle 1 to cycle 3 was considerably worse. In the case of untreated (BPEI/Ti3C2Tx)5, the pH sensitivity was similar to that of treated (BPEI/Ti3C2Tx)5. However, the initial resistance was an order of magnitude higher, and cyclability issues were also apparent.
The higher initial resistances of sensors assembled without the NaAsc treatment are attributed to oxidation of the untreated sensors prior to testing and during equilibration. The poor cyclability issues are likely caused by accelerated oxidation during testing, in which there was no residual NaAsc within the film. This leads to the conclusion that NaAsc can mitigate oxidation of the sensors (but not completely) and that Ti3C2Tx sensors treated with an antioxidant such as NaAsc are preferred.
Pure Ti3C2Tx sensors were assembled as a comparison as well. These were prepared by spraying a Ti3C2Tx dispersion onto PET to yield a film 98 nm thick. However, these sensors exhibited poor surface adhesion, similar to issues previously observed for pure Ti3C2Tx films.26 Due to the poor adhesion, spray-assembled sensors of pure Ti3C2Tx nanosheets were not tested further.
To compare against Ti3C2Tx-based sensors, rGO-based sensors were tested over the same pH range (Fig. S13†). The initial resistance of these sensors was an order of magnitude lower than that of the Ti3C2Tx counterparts, which we attributed to the higher thicknesses of the rGO-based sensors. As with Ti3C2Tx-based multilayer sensors, there was noticeable hysteresis when comparing cycles in which pH increased vs. decreased. For (BPEI/rGO) sensors, there were noticeable noise issues with the first cycle. As the noise issues were resolved by the second cycle, the first cycle was discarded and all other cycles were renumbered.
The overall responses of both types of rGO-based sensors were nonlinear and exhibited a significantly lower resistance change (<3 kΩ) over the entire tested pH range. Assuming a linear response (despite the obvious nonlinearity), the pH sensitivity of both rGO-based sensors was estimated as 0.6 kΩ pH−1. This was significantly lower than that of Ti3C2Tx-based sensors, but still in line with the expectation that Ti3C2Tx would be more pH-sensitive as compared to rGO because Ti3C2Tx has significantly more hydroxyl functional groups.
(3) |
Material | pH sensitivity | pH range | Reference |
---|---|---|---|
SWNT–PANI/PVA | 20 kΩ cm−2 pH−1 | 1–10 | 62 |
p-SWNT–PSS/PANI | 4.56 kΩ cm−2 pH−1 acidic region | 0.95–12 | 61 |
20.66 kΩ cm−2 pH−1 basic region | |||
Graphene | 2 kΩ pH−1 | 4–10 | 63 |
MWNT | 65 Ω pH−1 | 5–9 | 64 |
ES-PANI/PVB | 0.28 MΩ pH−1 | 1–8 | 65 |
Pd | 5% pH−1 | 4–10 | 66 |
MWCNT/Ni | 1% pH−1 | 2–10 | 67 |
(PDADMA/rGO)5 | 0.6 kΩ pH−1 | 3–7 | This work |
(BPEI/rGO)5 | 0.6 kΩ pH−1 | 3–7 | This work |
(PDADMA/Ti3C2Tx)5 | 23 kΩ pH−1 | 3–7 | This work |
40 kΩ cm−2 pH−1 | |||
19.4% pH−1 | |||
(BPEI/Ti3C2Tx)5 | 132 kΩ pH−1 | 3–7 | This work |
228 kΩ cm−2 pH−1 | |||
68.1% pH−1 |
There is variation in the literature on how pH sensitivity is reported, so we report our values here in these three ways (eqn (1)–(3)). pH sensitivities for (PDADMA/Ti3C2Tx)5 were 28 kΩ pH−1, 44 kΩ pH−1 cm−2, and 19.4% pH−1. pH sensitivities for (BPEI/Ti3C2Tx)5 are 132 kΩ pH−1, 228 kΩ pH−1 cm−2, and 68.1% pH−1. As compared to the other resistive sensors,61–67 the pH range of our Ti3C2Tx-based LbL sensors is generally narrower and restricted to acidic conditions. This is due to the hastened oxidation of Ti3C2Tx in basic environments.
Despite their smaller pH range, Ti3C2Tx-based LbL sensors exhibit considerably higher pH sensitivities as compared to other resistive sensors.61–64,66,67 As compared to single-walled carbon nanotube composites, the pH sensitivity is an order of magnitude higher.61,62 Both (PDADMA/Ti3C2Tx)5 and (BPEI/Ti3C2Tx)5 outperformed graphene-based sensors by one and two orders of magnitude, respectively.63 While the ES-PANI/PVB sensor had a higher reported sensitivity, the response was logarithmic and the same order of magnitude as (BPEI/Ti3C2Tx)5 sensors.59 Due to the logarithmic response, the actual sensitivity varies depending on what pH range the sensitivity is calculated over. As such, it is difficult to directly compare. We attribute our higher pH sensitivities to the abundance of surface functional groups on Ti3C2Tx and to the use of a pH-sensitive polymer.17,68,69 The proposed mechanism of pH sensitivity of graphene and other graphenic based sensors relies on interaction of the surface of graphene with OH− and H3O+ ions.7 As such, if there are more surface sites to interact with these ions, it is expected that the pH sensitivity will be higher. Cai et al. also demonstrated the benefits of the LbL structure on resistive sensor performance as compared to sensors with randomly oriented structures.24 As such, it is expected that sensors fabricated using LbL assembly will exhibit higher sensitivities than those assembled using less ordered assembly methods.63,64,66,67
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c9me00142e |
This journal is © The Royal Society of Chemistry 2020 |