Open Access Article
Clara Paolettia,
Maggie Heb,
Pietro Salvo
ac,
Bernardo Melaia,
Nicola Calisiade,
Matteo Mannini
de,
Brunetto Cortigianide,
Francesca G. Bellagambia,
Timothy M. Swagerb,
Fabio Di Francesco*a and
Andrea Pucci
*a
aDepartment of Chemistry and Industrial Chemistry, University of Pisa, Via G. Moruzzi 13, 56124 Pisa, Italy. E-mail: fabio.difrancesco@unipi.it; andrea.pucci@unipi.it
bDepartment of Chemistry, Institute for Soldier Nanotechnologies, Massachusetts Institute of Technology, 77 Massachusetts Avenue, Cambridge, MA 02139, USA
cInstitute of Clinical Physiology, National Council of Research (IFC-CNR), Via G. Moruzzi 1, Pisa, 56124, Italy
dDepartment of Chemistry “U. Schiff”, University of Florence, Via della Lastruccia 3-13, 50019 Sesto Fiorentino (FI), Italy
eNational Interuniversity Consortium of Materials Science and Technology (INSTM), Via G. Giusti 9, 50121 Firenze, Italy
First published on 1st February 2018
A new series of sidewall modified single-walled carbon nanotubes (SWCNTs) with perfluorophenyl molecules bearing carboxylic acid or methyl ester moieties are herein reported. Pristine and functionalized SWCNTs (p-SWCNTs and f-SWCNTs, respectively) were characterized by X-ray photoelectron spectroscopy (XPS), Raman spectroscopy and scanning electron microscopy (SEM). The nitrene-based functionalization provided intact SWCNTs with methyl 4-azido-2,3,5,6-tetrafluorobenzoate (SWCNT-N-C6F4CO2CH3) and 4-azido-2,3,5,6-tetrafluorobenzoic acid (SWCNT-N-C6F4CO2H) attached every 213 and 109 carbon atoms, respectively. Notably, SWCNT-N-C6F4CO2H was sensitive in terms of the percentage of conductance variation from 5 to 40 ppm of ammonia (NH3) and trimethylamine (TMA) with a two-fold higher variation of conductance compared to p-SWCNTs at 40 ppm. The sensors are highly sensitive to NH3 and TMA as they showed very low responses (0.1%) toward 200 ppm of volatile organic compounds (VOCs) containing various functional groups representative of different classes of analytes such as benzene, tetrahydrofurane (THF), hexane, ethyl acetate (AcOEt), ethanol, acetonitrile (CH3CN), acetone and chloroform (CHCl3). Our system is a promising candidate for the realization of single-use chemiresistive sensors for the detection of threshold crossing by low concentrations of gaseous NH3 and TMA at room temperature.
In particular, the detection of amines is important for industrial/environmental monitoring,11 food quality control12 and disease diagnosis.13 For example, in food quality control, the levels of ammonia (NH3), trimethylamine (TMA), dimethylamine and triethylamine can be used to assess the spoilage of fish.14 Devices capable of monitoring NH3 and TMA would enable quality validation throughout the food chain and identify those responsible for incorrect preservation. More specifically, fish is fresh if TMA remains below 10 ppm, whereas a concentration between 10 ppm and 50 ppm indicates preliminary rot, and above 60 ppm fish is considered rotten.15
To date, several studies have been performed concerning the development of chemical sensors sensitive to NH3 and TMA. Most of them involved the use of metal oxides working at temperatures above 200 °C.16,17 Recently, researchers have started combining the properties of metal-oxides and carbon nanomaterials, for example by decorating the surface of CNTs or graphene with metal-oxides nanoparticles.18 However, good results were only obtained at high temperatures and/or high concentrations of analyte.19 Notably, pristine carbon nanotubes (p-CNTs) change their conductivity upon the interaction with gas molecules,7 but the sensitivity and selectivity towards gas analytes are poor. Covalent or non-covalent modification of CNTs is an accessible procedure to provide graphitic materials with modulated functionalities and potential sensor response.6,20,21 Among the possible covalent functionalizations of CNTs, nitrene chemistry has proved to be an effective strategy under mild conditions being also useful for potential scale-up synthesis.22,23
In this work, we exploit the nitrene chemistry for the introduction on the SWCNTs surface of aziridinyl moieties that are able to provide an effective sensing response towards gaseous NH3 and TMA at room temperature. Notably, the degree of SWCNTs functionalization was determined by X-ray photoelectron spectroscopy (XPS), whereas Raman spectroscopy and scanning electron microscopy (SEM) assessed the structural integrity of CNTs after functionalization.
XPS analysis were performed as described by Salvo et al.24
1H and 19F NMR data were recorded on a Bruker AVANCE III HD 400 instrument at 400 MHz and 376 MHz, respectively. Chemical shifts are reported as δ values (ppm) and referenced to the residual protons of deuterated CDCl3. High resolution mass spectra were measured with a Bruker Daltonics APEXIV 4.7 Tesla FT-ICR-MS using ESI ionization.
Raman spectra were measured by a Horiba Jobin-Yvon LabRam (HR 800) Raman Confocal Microscope, with a laser excitation at 532 nm and a laser spot size of 1.2 μm. The Raman band peaks were calculated via Lorentzian curve fitting by the Levenberg–Marquardt algorithm.
Functionalized CNTs were characterized by SEM using a JEOL JSM-6700F field emission SEM (FESEM). CNTs analysis was performed using the public domain Image Tool 3.00 version image analyser program developed at the University of Texas Health Science Center in San Antonio and is available on Internet at http://ddsdx.uthscsa.edu/dig/itdesc.html.
An EmStat-MUX handheld potentiostat (PalmSens Instruments) was used to determine conductivity values from the sensor array.
A Fluke 287 True RMS (Fluke Corporation) was used as digital multimeter. Digital mass flow controllers (MFC) were from Sierra Instruments. A KINTEK gas generator system was used for gaseous VOCs detection measurements. Relative humidity was measured using a humidity meter (Extech).
The syntheses of methyl 4-azido-2,3,5,6-tetrafluorobenzoate (1) and of methyl 4-azido-2,3,5,6-tetrafluorobenzoic acid (2) were reported in the ESI.†
000 rpm for 20 min. The separated solid was re-dispersed in CHCl3 with the aid of ultrasonication and then recovered by centrifugation at 13
000 rpm for 15 min. The purification process was repeated four times. The final black solid (SWCNT-N-C6F4CO2CH3) was dried under vacuum at 70 °C overnight. An identical procedure was followed for the preparation of SWCNT-N-C6F4CO2H, by using 2.
Before the XPS analysis, some drops of analytical grade dichloromethane were added to dried samples. The solutions were sonicated for 5 min in an ultrasonic bath and the dispersion was immediately deposited on polycrystalline gold (about 100 nm thick) evaporated on mica. After the deposition, the samples were dried under nitrogen and annealed at 80 °C to remove the solvent and promote the sample adhesion to the substrate. XPS analysis was performed as detailed reported in the ESI.†
The analytes were delivered to the device at various concentrations (5–40 ppm) for steps of 100 s. For controlled humidity measurements, the gas mixture was bubbled through water before reaching the PTFE enclosure containing the device. The gas generator system was calibrated for each VOC of interest and used to deliver a known concentration of a given VOC diluted in N2 at a fixed gas flow rate to the device's enclosure. Relative humidity was also measured.
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| Fig. 1 Schematic reaction of SWCNTs with methyl-4-azido-2,3,5,6-tetrafluorobenzoate (1) and 4-azido-2,3,5,6-tetrafluorobenzoic acid (2) via nitrene addition. | ||
C (284.53–284.38 eV), C–C (285.5–285.11 eV), C–O/C–N (287.53–286.21 eV, our experimental setup did not allow these two components to be discriminated), C
O (287.92–286.45 eV), O–C
O (289.54–288.39 eV), and π–π (this component can be attributed to the delocalization of the electron on the surface of the nanotube). The C–F contribution was not found because of the interference with the π–π peak. Absorbed CO and CO2 within the porous structure of p-SWCNTs tubes possibly contributed to the carbonyl structure of the carbon peak.26
| Sample | Component | Peak position (eV) | FWHM (eV) | Sensitivity | Corrected area | Percentage |
|---|---|---|---|---|---|---|
| Pristine SWCNTs | F | — | — | 1 | 0 | 0.0% |
| O | 531.8 | 3.1 | 0.7 | 408 | 4.3% | |
| N | — | — | 0.5 | 0 | 0.0% | |
C C |
284.5 | 1.1 | 0.3 | 5963 | 63.2% | |
| C–C | 285.5 | 1.1 | 0.3 | 1297 | 13.7% | |
| C–O/C–N | 286.4 | 1.1 | 0.3 | 645 | 6.8% | |
C O |
287.6 | 1.1 | 0.3 | 453 | 4.8% | |
| COO | 288.9 | 1.1 | 0.3 | 338 | 3.6% | |
| π–π | 290.5 | 1.1 | 0.3 | 338 | 3.6% | |
| C total | — | — | 0.3 | 9034 | 95.7% | |
| SWCNTs-CO2CH3 | F | 687.8 | 2.2 | 1 | 336 | 1.7% |
O C |
531.6 | 1.9 | 0.7 | 1514 | 7.7% | |
| O–C | 533.2 | 1.9 | 0.7 | 523 | 2.7% | |
| O total | — | — | 0.7 | 2037 | 10.3% | |
| N | 400.3 | 1.8 | 0.5 | 1323 | 6.7% | |
C C |
284.5 | 1.1 | 0.3 | 6892 | 34.9% | |
| C–C | 285.3 | 1.1 | 0.3 | 3240 | 16.4% | |
| C–O/C–N | 286.2 | 1.1 | 0.3 | 2622 | 13.3% | |
C O |
287.3 | 1.1 | 0.3 | 1503 | 7.6% | |
| COO | 288.4 | 1.1 | v | 1179 | 6.0% | |
| π–π | 289.8 | 1.1 | 0.3 | 598 | 3.0% | |
| C total | — | — | 0.3 | 16 034 |
81.3% | |
| SWCNTs-CO2H | F | 687.9 | 2.0 | 1 | 231 | 0.9% |
O C |
531.6 | 2.1 | 0.7 | 1941 | 7.8% | |
| O–C | 533.5 | 2.1 | 0.7 | 650 | 2.6% | |
| O total | — | — | 0.7 | 2591 | 10.4% | |
| N | 400.3 | 1.9 | 0.5 | 1618 | 6.5% | |
C C |
284.5 | 1.1 | 0.3 | 8936 | 35.8% | |
| C–C | 285.3 | 1.1 | 0.3 | 4236 | 17.0% | |
| C–O/C–N | 286.3 | 1.1 | 0.3 | 3385 | 13.6% | |
C O |
287.4 | 1.1 | 0.3 | 1922 | 7.7% | |
| COO | 288.6 | 1.1 | 0.3 | 1324 | 5.3% | |
| π–π | 290.1 | 1.1 | 0.3 | 686 | 2.8% | |
| C total | — | — | 0.3 | 20 490 |
82.2% |
Fig. 2 shows the relative percentages of each component. After the functionalization, the C
C component dramatically decreased and the C–C and oxygenated components increased. The COO component was higher in the SWCNT-N-C6F4CO2CH3 than in the SWCNT-N-C6F4CO2H. This difference can be attributed to the higher functionalization ratio of SWCNT-N-C6F4CO2CH3, which was also confirmed from the area of fluorine peak.
![]() | ||
| Fig. 2 Relative percentages of the components found in the C 1s region in p-SWCNTs and f-SWCNTs after XPS analysis. | ||
Table 2 shows that in p-SWCNTs the percentages of F 1s and N 1s were 0%, whereas there was a very low percentage of oxygen (4.3%). In p-SWCNTs, the ratio between the component C
C and C–C was about 4.5. These data confirmed that the oxidation of the p-SWCNTs sample was very low with a high unsaturation degree. In SWCNT-N-C6F4CO2CH3 and SWCNT-N-C6F4CO2H, the percentages of F 1s were 1.7% and 0.9%, respectively, whereas the ratio between the components C
C and C–C decreased to about 2. In f-SWCNTs, the oxygen peak was higher than in p-SWCNTs. This result allowed the components O
C and O–C to be discriminated. Notably, the O
C component had an equal percentage of the component C
O, which confirmed the fitting goodness. The fitting goodness could not be determined for the O–C component, which could not be distinguished from the C–N component because of a similar binding energy.25
The N 1s percentage was high when compared with the F 1s percentage (every functional group had 1 atom of nitrogen and 4 atoms of fluorine). This result can be explained by a nitrogen contamination probably due to the residue of the solvent used in the functionalization reaction (N-methyl-2-pyrrolidone: NC5O). This residue affected not only the nitrogen area but also the carbon area. Therefore, using the area of F 1s to calculate the expected area of nitrogen associated with the functional groups, we corrected the carbon area to eliminate the solvent contribution. The functionalization ratio for the SWCNT-N-C6F4CO2H sample was 1 functional group every 213 carbon atoms of SWCNTs and in the SWCNT-N-C6F4CO2CH3 is 1 functional group every 109 carbon atoms of SWCNTs.
| Sample | D peak (cm−1) | G peak (cm−1) | ID/IG | D band FWHM (cm−1) |
|---|---|---|---|---|
| p-SWCNTs | 1333.2 ± 0.6 | 1591.3 ± 0.0 | 0.12 ± 0.01 | 30.5 ± 1.8 |
| SWCNT-N-C6F4CO2H | 1335.7 ± 1.5 | 1591.9 ± 0.0 | 0.06 ± 0.0 | 136.8 ± 5.0 |
| SWCNT-N-C6F4CO2CH3 | 1328.2 ± 1.6 | 1584.2 ± 0.2 | 0.04 ± 0.01 | 56.8 ± 9.0 |
The difference among f-SWCNTs is likely related to the strong Brønsted acid/base interaction of the carboxylic acid moiety with the lone-pair of the electron donor NH3 and TMA. Therefore, SWCNT-N-C6F4CO2H was the best candidate for the realization of NH3/TMA gas sensors, thus it was subject to further investigation. Fig. 5c and d show the response of three replicate sensors exposed to 5, 10, and 40 ppm of NH3 and TMA for 100 s each in air (<5% RH), respectively (3 exposures for each concentration). The sensor response time was about 2 min.
The decrease of conductance upon exposure can be explained considering the electronic nature of SWCNTs and their mechanisms of charge transfer. In the p-type semiconducting SWCNTs, the interaction with the donor molecules NH3 and TMA decreases the conductance of the network since the charge transfer from the amines effectively refills the holes in the valence band.30 This explains why p-SWCNTs are also sensitive to NH3 and TMA. The modification of the SWCNTs surface improves the interactions of the SWCNTs and enhances the electrical response.
Fig. 6a shows the calibration curves of SWCNT-N-C6F4CO2H in response to 100 s exposure of NH3 and TMA over the range of 5–40 ppm. The limit of detection was found to be 0.2 ppm, a value that placed the designed device at the topmost positions in amine sensing based on SWCNTs.31 The enhanced sensitivity was ascribed to the functionalization process that also contributes in removal of loose SWCNTs agglomerates with poor electrical contact and a more efficient transport of carriers. Moreover, our design involved a more simple but effective functional probes with respect to those reported in the recent literature and based on combination of Au nanoparticles or functionalized polyanilines.31
A typical linear behaviour is gathered from semi-log plots. The higher sensitivity of the sensor towards the detection of TMA relative to NH3 can be ascribed to its more basic nature, indicating a more favoured lone electron pair interaction with SWCNTs and the pendant N-C6F4CO2H groups.32 We observed a saturation above 40 ppm (not shown) that was most likely due to a strong interaction between the gas molecules and SWCNT materials.
We eventually checked the interference of other gases by observing the response of the sensor devices based on pristine and functionalized SWCNTs to a wide range of volatile organic compounds (VOCs) such as: benzene, tetrahydrofurane (THF), hexane, ethyl acetate (AcOEt), ethanol, acetonitrile (CH3CN), acetone and chloroform (CHCl3). Very low interferences were observed from all the organic vapours investigated with ΔG/G0 (%) values lower than 0.1 at 200 ppm of VOCs (three replicates per each of the CNTs, Fig. 6b), indicating the high selectivity of the sensors toward NH3 and TMA.
When NH3 or TMA interacts with the perfluorinated functionalizing molecule, a change organic molecular component to an anion can also lead to depletion or trapping of the holes of CNTs to reduce the system conductance.
Footnote |
| † Electronic supplementary information (ESI) available. See DOI: 10.1039/c7ra13304a |
| This journal is © The Royal Society of Chemistry 2018 |