Open Access Article
Tae Geun Joa,
Jae Min Jung*a,
Jiyeon Hanb,
Mi Hee Lim
b and
Cheal Kim
*a
aDepartment of Fine Chemistry, Department of Interdisciplinary Bio IT Materials, Seoul National University of Science and Technology, Seoul 139-743, Republic of Korea. E-mail: iamjemin@naver.conm; chealkim@seoultech.ac.kr; Fax: +82-2-973-9149; Tel: +82-2-970-6693
bDepartment of Chemistry, Ulsan National Institute of Science and Technology (UNIST), Ulsan 44919, Republic of Korea
First published on 31st May 2017
A sulfonate-based chemosensor 1 was designed and synthesized for sensing various analytes: Cu2+, Fe2+/3+ and Al3+. Sensor 1 showed a high selectivity and sensitivity for the analytes in a near-perfect aqueous medium. Cu2+ and Fe2+/3+ could be monitored by fluorescence quenching of 1. It had sufficiently low detection limits (1.25 μM for Cu2+ and 3.96 μM for Fe3+), which were below the recommended levels of the World Health Organization for Cu2+ (31.5 μM) and the Environmental Protection Agency for Fe3+ (5.37 μM). 1 showed the high preferential selectivity for Cu2+ and Fe3+ in the presence of competitive metal ions without any interference. Importantly, pyrophosphate could be used to distinguish Fe3+ from Cu2+. In addition, this sensor could monitor Al3+ through fluorescence emission change. Moreover, 1 was successfully applied to quantify and image Al3+ in water samples and living cells. Based on photophysical studies and theoretical calculations, the sensing mechanisms of 1 for Cu2+ and Al3+ were explained, respectively.
As the first most abundant metal ions in human body, iron plays crucial roles in numerous biological processes, including electron transport function, synthesis of hemoglobin and immune system.14–18 On the contrary, disruption of iron-ion homeostasis can induce a number of severe neurological diseases with diverse clinical manifestations, ranging from anemia to iron overload.19 Aluminum is the third most abundant element on earth and extensively used in food additives, pharmaceutical synthesis, cosmetics and the manufacturing industry.20–22 Due to its extensive use, aluminum can be easily accumulated in human body. Such accumulation of the metal ion could lead neuronal disorders such as Parkinson's disease and Alzheimer's disease.23–30 Therefore, the development of the chemosensors that could successfully recognize and determine these metal ions should be urgently developed.
In recent years, multiple target sensors for metal ions are attracting considerable interest, because they could abbreviate the processes to synthesize multiple compounds and facilitate to detect multiple analytes with a single device.3–7,11–13,16–18,20–22,31–36 However, there are still challenges to develop the sensors that could simultaneously detect and distinguish different target metal ions.
Sulfonic acid groups have been used to improve the solubility of chemosensors and naphthol moiety is a well-known excellent fluorophore.36–46 Therefore, we expected that the presence of a sulfonic acid group and a naphthol moiety in a chemosensor might not only increase its water solubility, but also have good optical properties.
Herein, we report the synthesis, characterization and fluorescent sensing behaviors of sulfonate-based sensor 1, triethylammonium (E)-3-hydroxy-4-(((2-hydroxynaphthalen-1-yl)methylene)amino)naphthalene-1-sulfonate. Sensor 1 could recognize selectively Cu2+ and Fe2+/3+ by the fluorescence quenching and Al3+ by the obvious fluorescence emission change. Based on UV-vis and fluorescence titrations, Job plots, ESI-mass analyses, 1H NMR titration and theoretical calculations, the sensing properties and mechanisms of 1 toward the three analytes were explained.
For Cu2+, 20 μL of each metal-ion solution (9 mM) was diluted to Bis–Tris buffer solution, respectively. 20 μL of Cu2+ solution (9 mM) was added to the solutions prepared above. Then, 9 μL of sensor 1 solution (10 mM) was added to the mixed solutions. Each vial had a total volume of 3 mL. After stirring them for a few seconds, fluorescence spectra were recorded at room temperature.
For Fe3+, 40 μL of each metal-ion solution (9 mM) was diluted to Bis–Tris buffer solution, respectively. 40 μL of Fe3+ solution (9 mM) was added to the solutions prepared above. Then, 9 μL of sensor 1 solution (10 mM) was added to the mixed solutions. Each vial had a total volume of 3 mL. After stirring them for a few seconds, fluorescence spectra were recorded at room temperature.
For Al3+, 67.5 μL of each metal-ion solution (100 mM) was diluted to Bis–Tris buffer solution, respectively. 67.5 μL of Al3+ solution (100 mM) was added to the solutions prepared above. Then, 9 μL of sensor 1 solution (10 mM) was added to the mixed solutions. Each vial had a total volume of 3 mL. After stirring them for a few seconds, fluorescence spectra were recorded at room temperature.
000 cells per 1 mL and then incubated at 37 °C for 12 h. For fluorescence imaging experiments, cells were first treated with 1 (dissolved in DMSO; 1% v/v final DMSO concentration; 20 μM; at room temperature) for 10 min. After incubation with aluminum nitrite (dissolved in water; 1% v/v DMSO; 200 μM) for 10 min, cells were washed with 2 mL of 10 mM Bis–Tris buffer (pH 7.4, 150 mM NaCl) two times. Imaging was performed with an EVOS FL fluorescence microscope (Life technologies) using a GFP light cube [excitation 470 (±11) nm; emission 510 (±21) nm].The fluorescence sensing ability of 1 was examined toward various metal ions such as Al3+, Ga3+, In3+, Zn2+, Cd2+, Cu2+, Fe2+, Fe3+, Mg2+, Cr3+, Co2+, Ni2+, Na+, K+, Ca2+, Mn2+ and Pb2+ in Bis–Tris buffer solution (10 mM, pH 7.0) (Fig. 1). Upon excitation at 380 nm, 1 exhibited a fluorescence emission at 442 nm. In the presence of most cations, there was no significant change in the fluorescence spectrum, whereas Cu2+, Fe2+, Fe3+ and Al3+ ions showed the notable spectral changes. In cases of Cu2+, Fe2+ and Fe3+, the emission intensity of 1 at 442 nm was completely quenched. Meanwhile, the fluorescence emission at 442 nm was red-shifted to 535 nm in the presence of Al3+. Therefore, 1 might be a potential fluorescence chemosensor that could detect copper and iron ions by fluorescence quenching and aluminum ion by fluorescence emission change.
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| Fig. 1 Fluorescence spectral change of 1 (30 μM) upon addition of 70 equiv. of different metal ions in Bis–Tris buffer (10 mM Bis–Tris, pH 7.0). | ||
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| Fig. 2 Fluorescence spectral change of 1 (30 μM) with Cu2+ ions (0–2.25 equiv.) in Bis–Tris buffer (10 mM, pH 7.0). | ||
In order to examine the binding stoichiometry of 1 with Cu2+, Job plot analysis was carried out (Fig. S3†). A maximum intensity appeared at the molar fraction of 0.5, which indicated a 1
:
1 binding mode between 1 and Cu2+. To further confirm the binding mode between 1 and Cu2+, ESI-mass spectrometry analysis was conducted (Fig. 3). The negative mass data of 1 for Cu2+ showed that the peak at m/z = 453.3 was assignable to 1–3H+ + Cu2+ [calcd, m/z: 453.0]. Based on the titration measurement, the association constant (K) of 1 with Cu2+ was calculated as 4.8 × 103 M−1 by Benesi–Hildebrand equation55 (Fig. S4†), which was within the range of those (103 to 1012) previously reported for chemosensors toward Cu2+.56–61 As shown in Fig. S5,† the detection limit (3σ/k)62 of 1 for Cu2+ was determined to be 1.25 μM which was much lower than that (31.5 μM) recommended by WHO in drinking water.63
A preferential selectivity of 1 toward Cu2+ was evaluated in the presence of other competitive species (Al3+, Ga3+, In3+, Zn2+, Cd2+, Fe2+, Fe3+, Mg2+, Cr3+, Co2+, Ni2+, Na+, K+, Ca2+, Mn2+ and Pb2+) (Fig. 4). There was no significant interference for sensing of Cu2+. For practical application, the pH effects of 1 in the absence and presence of Cu2+ were investigated at various pH range of 2 to 12. The fluorescence quenching of 1 by adding Cu2+ was observed between pH 6 and 10 (Fig. S6†), which warrants its application for detection of Cu2+ under physiological pH 7.0–8.4.64
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| Fig. 4 Fluorescence intensity (at 442 nm) of 1 upon addition of Cu2+ ions (2.0 equiv.) in the absence and presence of other metal ions (2.0 equiv.). | ||
Next, fluorescence titration of 1 toward Fe3+ was carried out to understand binding properties. Upon the addition of Fe3+, the fluorescence intensity at 442 nm was gradually reduced and completely quenched when 4 equiv. of Fe3+ were added (Fig. 5). UV-vis titration of 1 for Fe3+ showed that the absorption at 450 nm decreased and those at 300 and 580 nm increased with two clear isosbestic points at 405 and 527 nm (Fig. S7†). The peak at 580 nm, which has a high molar extinction coefficient (1.9 × 103 M−1 cm−1), are too large to be Fe-based d–d transitions. Thus, the new peak might be due to a metal-to-ligand charge-transfer (MLCT).65
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| Fig. 5 Fluorescence spectral change of 1 (30 μM) with Fe3+ ions (0–4.5 equiv.) in Bis–Tris buffer (10 mM, pH 7.0). | ||
Job plot analysis revealed a 1
:
1 stoichiometry for 1 and Fe3+ (Fig. S8†), which further was confirmed by ESI-mass spectrometry analysis. As shown in Fig. 6, the negative mass data of 1 for Fe3+ showed the major peak at m/z = 508.0, which was assigned to 1–3H+ + Fe3+ + NO3− [calcd, m/z: 508.0]. The association constant (K) for Fe3+ was determined to be 1.1 × 104 M−1 by using Benesi–Hildebrand equation55 (Fig. S9†), which was within the range of those (103 to 105) previously reported for chemosensors toward Fe3+.66 The detection limit (3σ/k)62 of 1 for Fe3+ was calculated to be 3.96 μM (Fig. S10†), which was lower than the guideline (5.37 μM) recommended by environmental protection agency guideline (EPA) for iron in drinking water.63 To examine the preferential selectivity for Fe3+, the interference experiments were evaluated in the presence of other competitive species (Fig. 7). Compared with the fluorescence intensity of 1–Fe3+, there was no distinct variation in the presence of other metal ions. These results suggested that sensing properties of 1 for Fe3+ was hardly affected from potentially competitive metal ions. The pH sensitivity of Fe3+ detection by 1 was examined at various pH range of 2 to 12 (Fig. S11†). The fluorescence quenching of the 1–Fe3+ complex was exhibited between pH 2 and 10, which warrants that Fe3+ could be clearly detected by fluorescence measurements using chemosensor 1 over a wide range of pH.
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| Fig. 7 Fluorescence intensity (at 442 nm) of 1 upon addition of Fe3+ ions (4.0 equiv.) in the absence and presence of other metal ions (4.0 equiv.). | ||
On the other hand, we also conducted the UV-vis titration of 1 for Fe2+ (Fig. S12†). The titration for Fe2+ was nearly identical to that of Fe3+. These results could be explained by the rapid oxidation reaction of Fe2+ to Fe3+ in the 1–Fe2+ complex by oxygen molecule.28 To further verify our proposal, the UV-vis spectral changes of 1 for Fe2+ were observed under the degassed conditions (Fig. S13†). Upon the addition of Fe2+ into a solution of 1 under an anaerobic condition, there was no significant change in spectrum of 1. Upon the exposure of 1–Fe2+ complex to air, however, the spectrum of 1–Fe2+ complex was dramatically changed, which was nearly identical to that of 1–Fe3+ complex. These observations indicated that 1–Fe2+ complex formed under the degassed conditions might be rapidly oxidized to 1–Fe3+ complex in air.
Some metal complexes showed the selectivity toward specific anions in the systems such as Cu–S, Cu–CN, and Hg–I.67 Therefore, we also examined the selectivity of 1–Fe3+ and 1–Cu2+ complexes toward various anions, such as PPi (pyrophosphate), AMP, ADP, ATP, CN−, AcO−, F−, Cl−, Br−, I−, BzO−, N3−, SCN−, H2PO4−, S2−, NO3− and SO42− (Fig. S14†). Only PPi induced a recovery of fluorescence intensity toward 1–Fe3+ complex, while there was no change in fluorescence intensities of 1–Fe3+ and 1–Cu2+ complex solutions. It is worthwhile to mention that the fluorescence recovery of 1–Fe3+ complex by PPi is very useful, because it could distinguish 1–Fe3+ from 1–Cu2+ complex. As shown in Fig. 1, both 1–Fe3+ and 1–Cu2+ complexes exhibited the fluorescence quenching. If sensor 1 with the strong fluorescence intensity would show fluorescence quenching upon the addition of a certain metal ion, it can be Cu2+ or Fe ion. In such a case, the fluorescence recovery of 1 by PPi would indicate that the metal ion could be Fe ion, while in the absence of the fluorescence recovery of 1 it could be Cu2+.
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| Fig. 8 Fluorescence spectral change of 1 (30 μM) with Al3+ ions (0–80 equiv.) in Bis–Tris buffer (10 mM, pH 7.0). | ||
The Job plot analysis68 for 1 and Al3+ showed a 1
:
1 complexation (Fig. S16†). The binding mode of 1 and Al3+ was further confirmed by ESI-mass spectrometry analysis (Fig. S17†). The negative mass spectrum of 1 for Al3+ showed that the major peaks at m/z = 479.3 and 556.5 were assignable to 1–3H+ + Al3+ + NO3− [calcd, m/z: 479.0] and 1–3H+ + Al3+ + NO3− + DMSO [calcd, m/z: 557.0], respectively. Based on the fluorescence titration, the association constant (K) of 1 for Al3+ derived from Benesi–Hildebrand equation55 was calculated to be 8.9 × 10 M−1 (Fig. S18†), which was within the range of those (102 to 109) previously reported for Al3+-binding chemosensors.69 The detection limit (3σ/k)62 of 1 as a fluorescence sensor for Al3+ sensing was determined to be 18.07 μM (Fig. S19†).
In order to confirm the selectivity of 1 for Al3+ over competing metal ions, the interference experiments were carried out (Fig. S20†). In the presence of Cu2+, Fe2+, Fe3+ and Cr3+, the relative emission intensity was inhibited, whereas most of other metal ions did not interfere with the detection of Al3+. The practical application of 1 was evaluated through pH dependent study. As shown in Fig. S21,† 1 could clearly detect Al3+ over a wide range of pH 4.0–11.0. To further check the practical applicability of sensor 1, we conducted the real sample analysis for quantitative measurement of Al3+. A good calibration curve was constructed for the determination of Al3+ (Fig. S22†). Then, it was applied to determinate Al3+ ions in both artificial polluted and drinking water samples. As shown in Table 1, suitable recoveries and Relative Standard Deviation (R.S.D.) values of the water samples were obtained.
| Sample | Al(III) added (μmol L−1) | Al(III) found (μmol L−1) | Recovery (%) | R.S.D (n = 3) (%) |
|---|---|---|---|---|
| a Condition: [1] = 30 μmol L−1 in Bis–Tris buffer (10 mM, pH 7.0).b Prepared by deionized water, 300 μmol L−1: Zn2+, Cd2+, Pb2+, Hg2+, Na+, K+, Ca2+, Mg2+. | ||||
| Artificial polluted waterb | 300.0 | 303.8 | 101.3 | 1.40 |
| Drinking water | 300.0 | 296.9 | 99.0 | 0.96 |
To investigate the sensing mechanism of 1 toward Al3+, 1H NMR titration of 1 with Al3+ was carried out (Fig. 9). Upon the addition of Al3+, the protons H1 and H2 disappeared, and the protons H3, H5 and H8 shifted slightly up-field. When more than 1 equiv. of Al3+ were added, there was no shift in the position of proton signals, which implied the 1
:
1 complexation of 1 with Al3+.
To examine the potential of 1 to monitor Al3+ in living cells, fluorescence imaging experiments were conducted (Fig. 10). HeLa cells were first incubated with 1 for 10 min and then exposed to aqueous Al3+ solution for 10 min before imaging. The results showed that the HeLa cells without either Al3+ or 1 showed negligible intracellular fluorescence, while those cultured with both Al3+ and 1 exhibited fluorescence.
:
1 stoichiometry for the 1–Cu2+ and 1–Al3+ complexes. Moreover, for the simplicity of the calculations, the triethylammonium salt of 1 was replaced by a hydrogen atom (Fig. 11). The energy-minimized structures for 1, 1–Cu2+ and 1–Al3+ complex were calculated by utilizing the density functional theory (DFT/B3LYP/main group atom and Al: 6-31G** and Cu: Lanl2DZ/ECP) (Fig. 11). The energy-minimized structure (1C, 2C, 3N, 4C = 128.9°) of 1 showed a twisted shape (Fig. 11a). After combined with Cu2+ or Al3+, the structures of the complexes 1–Cu2+ and 1–Al3+ were flatter than that of 1 (1C, 2C, 3N, 4C = 157.0° for Cu2+ and 1C, 2C, 3N, 4C = 162.6° for Al3+) (Fig. 11b and c). Both Cu2+ and Al3+ were coordinated to the N atom in the Schiff-base and the two O atoms in the hydroxyl groups of 1.
We further investigated the singlet excited states of 1, 1–Cu2+ and 1–Al3+ species by using the TD-DFT (time dependent-density functional theory) methods, which were compared with their UV-vis spectra. In case of 1, the main molecular orbital (MO) contribution of the first lowest excited state was determined for HOMO → LUMO transition (424.0 nm, Fig. S23†), which was characterized by intramolecular charge transfer (ICT) transition. For 1–Cu2+, the main MO contributions of the 10th excited state were determined for HOMO (α) → LUMO (α) and HOMO (β) → LUMO+1 (β) transitions with predominant ICT (474.0 nm, Fig. S24†). These results were consistent with the bathochromic shift in the UV-vis spectra of 1 and 1–Cu2+ complex. The remainder of the MO contributions was determined for ligand-to-metal charge-transfer (LMCT).70,71 The charge-transfer might provide a pathway for non-radiative decay of the excited state, which induced the quenching of fluorescence of 1. For 1–Al3+, the main MO contribution of the first lowest excited state was determined for HOMO → LUMO transitions (492.0 nm, Fig. S25†), which indicated ICT transition. There was no obvious change in the electronic transition between 1 and 1–Al3+ complex, while only the decrease of energy gap (424.0–492.0 nm) was observed upon chelating of 1 with Al3+. These results suggested that the sensing mechanism of 1 toward Al3+ was originated from enhancement of ICT, which caused the red-shift of the emission maximum of fluorescence from 442 nm to 535 nm.72 From the Job plots, ESI-mass spectrometry analyses and theoretical calculations, we proposed the binding structures of 1–Cu2+, 1–Fe3+ and 1–Al3+ complexes in Schemes 2 and 3.
Footnote |
| † Electronic supplementary information (ESI) available: Experimental procedures and additional experimental data. See DOI: 10.1039/c7ra05565j |
| This journal is © The Royal Society of Chemistry 2017 |