Ritu
Ladhi
,
Arshminder Kaur
Dhillon
and
Monika
Singh
*
Institute of Nano Science and Technology, Knowledge City, Sector-81, Mohali-140306, Punjab, India. E-mail: monika@inst.ac.in
First published on 8th April 2024
Ultrathin 2D metal–organic frameworks (MOFs) exhibit a myriad of unparalleled properties, rendering them extensively applicable across various fields. Despite this, developing a 2D MOF sensor for detecting hazardous amines in water remains a formidable challenge. To address this issue, we synthesized Ni-btc MOF ultrathin nanosheets with a thickness of approximately 4.15 nm for the detection of amines in water. These nanosheets demonstrated a notable “turn-on” fluorescence response in the presence of ammonia and aliphatic amines. The detection limit for aliphatic amines ranged from 297 to 424 nM, while for ammonia, it reached an impressive low limit of around 42 nM, which is an excellent value compared to other reported MOFs for ammonia sensing in water. Density functional theory calculations elucidated the mechanism underlying fluorescence enhancement. Additionally, a mixed matrix membrane based on MOF nanosheets was fabricated for real-time sensing that exhibits an immediate color change in the presence of ammonia and aliphatic amines.
So far, various analytical techniques, including mass spectrometry,6 electrosensing,7 high-performance liquid chromatography,8 gas chromatography,9 and capillary electrophoresis10 have been employed for the analysis and quantification of amines.11–13 However, numerous existing methodologies involve expensive and bulky equipment, intricate procedures, and long hours of testing times, rendering them unsuitable for rapid and efficient analysis.14 In contrast, optical sensing offers rapid and real-time analytical capability based on changes in fluorescence intensity. For any sensor to be viable for real-time application, along with rapid and high sensitivity, hydrolytic and thermal stability are crucial parameters.15–22 Metal–organic frameworks (MOFs) have emerged as the most suitable choice for such sensing applications.23
Metal–organic frameworks (MOFs) are porous inorganic and organic hybrid solids. Currently, 2D MOF nanosheets are gaining more popularity compared to their 3D bulk counterparts. 2D MOFs offer numerous exposed active sites, ultrahigh surface-to-volume atomic ratios, and larger specific surface area, which are advantageous for performance enhancement in various applications such as sensing, catalysis, gas separation, and storage.24 Therefore, 2D MOFs are the ultimate package with MOF and 2D nanomaterial properties. Some studies have emphasized the remarkable potential of 2D MOF nanosheets in the fabrication of fluorescent sensors.25–27 Recently, Guo and his co-workers employed the ‘top-down’ ultrasonic exfoliation method to synthesize nanosheets of Cd MOF using 4,4′-((2,5-dimethoxy-1,4-phenylene)bis(ethene-2,1-diyl))dibenzoic acid as the organic linker. They showcased the significant enhancement of sensing and fluorescence properties in MOF nanosheets compared to those in bulk materials for the detection of glyphosate (Glyph) with fast response and low detection limit in water.28 Using a self-assembly strategy, Wong and co-workers synthesized Zn–BTC MOF nanosheets for colorimetric and fluorometric sensing of ammonia. They incorporated ZnQ to tune the properties of Zn–BTC nanosheets, which enhanced ammonia detection with a limit of detection value of 0.27 ppm in the gaseous phase and 60.8 nm in the liquid phase.29 However, reports on the utilization of 2D nanostructured MOF for amines sensing in water are relatively scarce.
Herein, we employed a surfactant-free approach for the synthesis of ultrathin MOF nanosheets (NS) for ammonia and aliphatic amines sensing in water. At present, diverse methods are being utilized including surfactant-assisted techniques,30 ultrasonication exfoliation,31 interfacial synthesis,32 and modulated technique33 for MOF NS synthesis. However, each of these approaches possesses certain limitations such as the involvement of complex synthesis processes that are more time-consuming, and the possibility of structural deterioration. Therefore, using a surfactant-free method involving a 2D oxide sacrifice approach (2dOSA) for synthesizing ultrathin MOF nanosheets is more beneficial compared to other methods. In this approach, amorphous NiO NS were initially synthesized, which serve as sacrificial templates that facilitated the formation of Ni MOF NS through coordination with the 1,3,5-benzene tricarboxylic acid (BTC) ligand. These MOF NS exhibited remarkable “turn-on” fluorescence in the presence of ammonia and aliphatic amines and can detect as low as 41.8 nM concentration of ammonia.
To enhance the practical usability of Ni-btc NS, we also synthesized MOF-based flexible and recyclable mixed matrix membranes (MMMs), demonstrating their vapochromic sensing capabilities. This underscores the excellent ability of our MOF's NS to sense amines in both solution and vapor states, presenting the potential for utilizing 2D MOF NS as an effective device for real-time ammonia and aliphatic amines detection.
), and (31
) planes of the Ni-btc MOF structure.34 The presence of key functional groups in MOF NS was confirmed through FT-IR spectroscopy (Fig. S3a†), where bands around 3431–3106 cm−1 are the stretching vibration of the O–H group of H2O molecules. Peaks around 1606–1514 cm−1 and 1424–1351 cm−1 correspond to the asymmetric and symmetric stretching vibrations of COO−. Vibrational bands at 1108 cm−1 indicated in-plane C–C stretching, while those between 810–712 cm−1 signified the C–H aromatic groups (out of plane) stretching vibrations.36
UV-Vis spectra (Fig. S3b†) exhibited an absorbance band between 230–295 nm, attributed to n–π* and π–π* intra-ligand transitions of the btc ligand. Additionally, a broad absorbance peak around 400 nm and 550 nm was observed, indicating Ni d–d transitions.37 Fig. S4† displays the nitrogen sorption isotherm of Ni-btc NS with a Brunauer–Emmett–Teller (BET) surface area of 39 m2 g−1. Thermal stability analysis using TGA (Fig. S5†) unveiled a two-step decomposition process of the MOF NS. During the initial phase, between 100 °C and 250 °C, the crystallized water molecules evaporate. Subsequently, in the second step between 250 °C and 400 °C, the organic ligand decomposes.38
X-ray photoelectron spectroscopy (XPS) and energy-dispersive X-ray spectroscopy (EDS) mapping were also employed to further confirm the successful formation of Ni-btc NS. The XPS survey spectrum showed the presence of C 1s, O 1s, and Ni 2p elements, with binding energies at 284.8, 532.08, and 855.98 eV, respectively (Fig. S6a†). The deconvoluted C 1s spectrum of Ni-btc NS (Fig. S6b†) featured peaks at 289.58, 288.33, 285.19, and 284.51 eV, assigned to O–C
O, C
O, C–OH, and C–C peaks, respectively. The deconvoluted O 1s spectrum (Fig. S6c†) showed binding energies at 533.65, 532.94, 531.76, and 531.20 eV corresponding to O–H, O–C
O, C
O, and C–OH species, respectively. Furthermore, the Ni 2p deconvoluted spectrum (Fig. S6d†) indicated the presence of Ni+2 with peaks at 874.02 eV and 856.5 eV, along with two satellite peaks at 879.02 and 860.9 eV.36 The EDS mapping also indicates the presence of Ni and O elements in NiO NS (Fig. S7†) and Ni, O, and C elements in Ni-btc NS (Fig. S8†).
Thereafter, we examined fluorescence sensing of MOF NS towards amines, namely, ammonia (NH3), methylamine (MA), triethylamine (TEA), and di-isopropylamine (DIPA) in aqueous medium. Initially, MOF NS suspensions were prepared in water (2 mg in 2 mL), then for fluorescence studies, 100 μM of each amine (5 mM) was added in an incremental fashion to the above suspension (500 μL). A dramatic increase in fluorescence intensity of Ni-btc NS was observed with the addition of amines (Fig. S10a, S11a and S12a†). These results were even more pronounced with ammonia, which showed a remarkable turn-on effect even with the addition of 2 μM concentration (Fig. 2a). The limit of detection was measured using the equation 3σ/m, where σ is the deviation from the standard values calculated for five blank emission intensities of MOF NS, and m represents the slope derived from the linear regression curve fitting of the intensity against concentration. The LODs were found to be 297 nM for MA, 424 nM for TEA, and 330 nM for DIPA (Fig. S10b, S11b and S12b,† respectively), which are exceptionally low from most of the other reported values (Table S4†). NH3 exhibited a LOD value of 41.8 nM (Fig. 2b), which is the lowest among other reports for aqueous ammonia detection (Table S3†). There are limited reports in the literature on the detection of ammonia and aliphatic amines in an aqueous medium, and to the best of our knowledge, there is no previous report on using MOF NS as a sensor material for “turn-on” ammonia and aliphatic amines sensing in aqueous medium.
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| Fig. 3 PXRD patterns of Ni-btc NS before and after immersing in amines and ammonia solution for 24 h. | ||
The fluorescence lifetime of MOF NS, after the addition of various analytes, was recorded and it showed no significant change in lifetime (Fig. S14 and Table S1†).
The phenomenon of fluorescence enhancement is completely opposite to fluorescence quenching. Previous studies suggest that in the case of electron-deficient analytes, the electrons from the LUMO/conduction band of the MOF are transferred to the LUMO of the analyte, which results in fluorescence quenching. Conversely, for electron-rich analytes, the excited electrons shift from the LUMO of the analyte to the conduction band (CB) of the MOF, leading to enhanced radiative emission.40 In our case, the analytes are electron-rich amines and upon comparing the LUMOs of amines and Ni-btc NS, the amines (Fig. S17†) exhibited a higher LUMO energy level than that of the MOF. Consequently, upon photoexcitation, electrons would migrate from the LUMO of the amines to the LUMO of the MOF, making it more populated, and hence resulting in fluorescence enhancement.
The expected order of fluorescence enhancement in general, is correlated with the lower LUMO of the amine, i.e. amine with the lower LUMO will be able to transfer more electrons to MOF and should show more enhancement in fluorescence. However, our findings deviate from this trend of LUMO energies, with the order of fluorescence enhancement being NH3 (67.1%) > MA (44.6%) > DIPA (40.4%) > TEA (33.1%) (Fig. S13†). This deviation indicates the influence of other factors, such as dipole–dipole interactions and hydrogen bonding between the amines and the MOF.26 As our MOF NS are not highly porous (Fig. S4†), only surface interactions are possible. Therefore, electron-rich analytes can undergo dipole–dipole interactions with the MOF ligand, which leads to the phenomenon of electron transfer. Each amine has a different extent of interaction with Ni-btc NS depending upon its size and dipole moment. The calculated dipole moments of different amines (Fig. S18†) are in correlation with the order of fluorescence enhancement, i.e. more dipole moment leads to more interaction with Ni-btc NS and hence, more increase in fluorescence. Among all, NH3 has the maximum dipole moment, therefore, it has the highest fluorescence enhancement and this aligns well with the experimental results.
To assess the membrane's recyclability towards NH3, five consecutive exposure and regeneration experiments were conducted, followed by post-PXRD and FESEM analyses. Fig. S21† demonstrates the membrane's consistent colorimetric sensing across the five cycles, highlighting its remarkable recyclability. Post-exposure PXRD analysis after five cycles, showed peak broadening and decrease in peak intensity, indicating a gradual loss of MOF NS crystallinity over time. However, notably, no additional peaks were observed, signifying the stability of the Ni-btc NS MMM even after prolonged (Fig. S22†). We have also examined the morphology of the membrane (Fig. S23†), revealing an increase in surface roughness, that was also observed in PXRD studies.
Furthermore, we conducted on-site ammonia detection using the well-known reaction between ammonium chloride and sodium hydroxide, which releases ammonia along with water and sodium chloride. The membrane was placed inside a round-bottom flask containing ammonium chloride and sodium hydroxide reactants. As the reaction progressed, the membrane exhibited a distinct color change within a few minutes (Fig. S24†). This straightforward organic reaction validates the ability of Ni-btc NS to sense ammonia under real-time conditions.
To test the real-life sensing applicability of Ni-btc NS, we performed an experiment with a model of contaminated wastewater.15 Fig. S25† demonstrates a relative increase in fluorescence of Ni-btc NS in wastewater, upon the addition of different concentrations of NH3, highlighting the material's good sensitivity towards NH3 even in the presence of other ions in the wastewater, with the high recovery percentage (see Table S5†).
Footnote |
| † Electronic supplementary information (ESI) available: PXRD, TGA spectra, SEM images, PL spectra of MOF and MMM etc. See DOI: https://doi.org/10.1039/d4nr00546e |
| This journal is © The Royal Society of Chemistry 2024 |