Open Access Article
Jitendra P.
Nandre
a,
Samadhan R.
Patil
a,
Suban K.
Sahoo
b,
Chullikkattil P.
Pradeep
c,
Andrei
Churakov
d,
Fabiao
Yu
e,
Lingxin
Chen
*e,
Carl
Redshaw
f,
Ashok A.
Patil
*a and
Umesh D.
Patil
*g
aDepartment of Chemistry, Z. B. Patil College, Deopur, Dhule – 424 002, MS, India
bDepartment of Applied Chemistry, S. V. National Institute Technology, Surat-395007, Gujrat, India
cSchool of Basic Sciences, Indian Institute of Technology Mandi, Mandi, Himachal Pradesh 175001, India
dInstitute of General and Inorganic Chemistry, Russian Academy of Sciences, Leninskii prosp. 31, Moscow 119991, Russian Federation
eKey Laboratory of Coastal Zone Environmental Processes and Ecological Remediation, Yantai Institute of Coastal Zone Research, Chinese Academy of Sciences, Yantai, Shandong 264003, China
fDepartment of Chemistry, School of Mathematics and Physical Sciences, University of Hull, Cottingham Road, Hull, HU6 7RX, UK
gDepartment of Chemistry, S.S.V.P.S's L. K. Dr P. R. Ghogrey Science College, Dhule-424 001, MS, India
First published on 19th September 2017
The pyridine substituted thiourea derivative PTB-1 was synthesized and characterized by spectroscopic techniques as well as by single crystal X-ray crystallography. The metal ion sensing ability of PTB-1 was explored by various experimental (naked-eye, UV-Vis, fluorescence, mass spectrometry and 1H NMR spectroscopy) and theoretical (B3LYP/6-31G**/LANL2DZ) methods. PTB-1 exhibited a highly selective naked-eye detectable color change from colorless to dark brown and UV-Vis spectral changes for the detection of Ag+ with a detection limit of 3.67 μM in aqueous medium. The detection of Ag+ ions was achieved by test paper strip and supported silica methods. In contrast, PTB-1 exhibited a 23-fold enhanced emission at 420 nm in the presence of Hg2+ ions with a nano-molar detection limit of 0.69 nM. Finally, the sensor PTB-1 was applied successfully for the intracellular detection of Hg2+ ions in a HepG2 liver cell line, which was monitored by the use of confocal imaging techniques.
Additionally, mercury has been considered as the most toxic metal ion amongst the heavy transition metal ions to humans,13–15 and causes severe neurotoxic, immunotoxic and genotoxic effects. Mercury contamination of ecosystems occurs through a number of sources, which include volcanic and oceanic discharges, burning of fossil fuels and solid waste incineration.16,17 Mercury can be accumulated in the human body through the food chain. When it is accumulated in the human body, it can cause serious and lasting damage to the kidneys, endocrine system, brain, nervous system and immune system when present at a very low concentration.18,19
At present, a number of methods have been developed to detect Ag+ and Hg2+ ions such as inductively coupled plasma detectors, inductively coupled plasma mass spectrometry (ICP-MS), fluorescence anisotropy assays, quantum dot based assays, atomic absorption spectrometry (AAS) and inductively coupled plasma atomic emission spectrometry (ICP-AES).20–22 Although these technologies can detect Ag+ and Hg2+ ions selectively with high sensitivity, they require exclusive and sophisticated instrumentation, highly trained hands and complex sample-preparation steps, which are major blockages in their everyday use. In contrast, the naked-eye detection method allows detection up to micro/submicromolar levels and that too without involving any expensive/sophisticated instruments. Silver and mercury are normally found as ions (Ag+ and Hg2+) in water. Therefore, there is a high demand for highly selective and sensitive chemosensors for detecting Ag+ and Hg2+ ions from aqueous solution. However, most of the previously reported chemosensors for this purpose have a number of downsides viz. poor detection limit, tedious synthetic procedures, intervention from other transition metal ions, long response times, use of organic solvents, and most of the reported sensors are selective only for either Ag+ or Hg2+ ions (Table S1†).
Furthermore, the fluorescence sensing of cations, such as Hg2+, Fe3+, Pb2+ and Cu2+, is a particularly challenging task since these ions mostly act as quenchers via electron transfers and facilitated intersystem crossing processes. Therefore, it remains a challenge to develop a “turn-on” fluorescence sensor for Hg2+ that can be applied in aqueous medium and applied to living systems. Although there are several sensors capable of recognizing Ag+ and Hg2+ ions individually, to the best of our knowledge, only around 5–10% of them are selective and sensitive for both. Additionally, among the reported sensors, most of them are chemodosimeters for Hg2+ ions. Thus, the development of sensitive and selective methods for the determination of trace amounts of Ag+ and Hg2+ ions in aqueous media is of considerable importance for both environmental protection and human health. From the literature, we also note that the presence of sulfur (as a soft Lewis base) is highly desirable in the ligands to be utilized for Ag+ and Hg2+ ion recognition.
Considering the above facts and as a part of our on-going research on the design and synthesis of chemosensors,23–27 we report herein a new pyridine substituted thiourea based sensor PTB-1 (Scheme 1) for the selective and sensitive detection of Ag+ and Hg2+ ions from 100% aqueous solution.
:
H2O (20
:
80, v/v)] turned dark brown selectively only in the presence of Ag+ among the other tested metal ions (Cs+, Ba2+, Hg2+, K+, Li+, Cu2+, Cd2+, Al3+, Co2+, Cr3+, Mg2+, Na+, Ni2+, Fe2+, Fe3+, Mn2+, Ca2+, Pb2+ and Zn2+ (200 μL, 1 × 10−2 M, in H2O)). No significant color change of PTB-1 was observed in the presence of the other examined cations even when present in excess, except for Hg2+ which exhibited a slight yellow coloration. These results clearly indicated the selective colorimetric response of PTB-1 towards Ag+. Furthermore, the concentration dependent naked-eye sensing of Ag+ ions was performed (Fig. S5†), and we observed visible color changes from colorless to brown, even at a low concentration i.e. up to 5 × 10−4 M of Ag+ ions. Encouraged by these Ag+ responses shown by PTB-1, the qualitative and quantitative metal ion sensing ability of PTB-1 was determined further by the use of spectrophotometric methods.
![]() | ||
Fig. 2 Photograph of the vials containing PTB-1 [2 mL, 5 × 10−4 M, in CH3OH : H2O (20 : 80, v/v)] in the presence of 2 equivalents of different tested metal cations (200 μL, 1 × 10−2 M, in H2O). | ||
:
H2O (20
:
80, v/v) (2 mL, 4 × 10−5 M) in the absence and presence of 5 equivalents of different metal cations (40 μL, 1 × 10−2 M, in water) are shown in Fig. 3A. The absorption bands of PTB-1 were significantly and selectively affected by the addition of Ag+ ions. The receptor PTB-1 has two distinct absorption bands at 210 nm and 265 nm. Upon addition of Ag+ ions, the absorption bands of PTB-1 at 210 nm and 265 nm were merged together and appeared as a broad band having an absorption maximum at 243 nm along with the advent of a broad band between 350 and 600 nm. This observed wide-ranging band between 350 and 600 nm is responsible for the generation of the dark brown color. A slight spectral change of PTB-1 was observed with Hg2+ with the appearance of a new broad absorption band having a maximum at 214 nm. However, no noticeable spectral changes were observed with the other tested cations.
To gain more insight into the cation chemosensing properties and the mechanism of PTB-1, an absorption titration was performed with Ag+ ions. As shown in Fig. 3B, upon sequential addition of Ag+ ions (0–10 equivalent, 1 × 10−3 M, in H2O) to the PTB-1 solution [2 mL, 4 × 10−5 M, in CH3OH
:
H2O (20
:
80, v/v)], the intensity of the absorption band centered at 243 nm was uninterruptedly amplified with the diminishing of the band at 265 nm. Also, a new broad band appeared between 350 and 600 nm. From the absorption titration data, a linear dependence of absorption at 243 nm was observed as a function of the Ag+ concentration (Fig. S6†), and thereby the stoichiometry of PTB-1 with Ag+ could be estimated to be 1
:
2. Moreover, the mole ratio plot (Fig. S7†) and the Job's plot (Fig. 4) support the formation of a complex between PTB-1 and Ag+ in a 1
:
2 binding stoichiometry. Furthermore, direct evidence for the formation of a 1
:
2 complex was obtained from the ESI-MS spectra of PTB-1 in the presence of 2.0 equivalents Ag+ in methanol/water (20
:
80, v/v) (Fig. S8†). The main characteristic MS peak was observed at m/z = 258.0714 ([PTB-1 + H]+) for pure PTB-1. However, on addition of 2.0 equivalents of Ag+, the peak at 258.0714 disappeared and a new peak appeared at m/z = 491.2671 corresponding to the complex [{(PTB-1)–2H + 2Ag} + Na]+.
![]() | ||
Fig. 4 Job's plot for determining the 1 : 2 stoichiometry of PTB-1 [4 × 10−5 M, in CH3OH : H2O (20 : 80, v/v)] and Ag+ ions (4 × 10−5 M, in H2O). | ||
Based on the 1
:
2 stoichiometry for PTB-1·Ag+ complexation, the binding constant (Ka) of PTB-1 with Ag+ was determined using the Benesi–Hildebrand plot analysis,31 by using eqn (1).
![]() | (1) |
where, A and A0 are the absorbance of the PTB-1 solution in the presence and absence of Ag+ ions, Amax is the saturated absorbance of PTB-1 in the presence of excess amounts of Ag+, and [Ag+] is the concentration of Ag+ ions added (mol L−1). Finally, the plotting of 1/ΔA vs. 1/[Ag+] showed a linear relationship (Fig. S9†), and the binding constant (Ka) was determined from the slope and was estimated to be 15
963 M−1 for the PTB-1·Ag+ complexation.
Furthermore, the limit of detection (LOD) and limit of quantification (LOQ) of the receptor PTB-1 were calculated. According to the IUPAC definition, the LOD and LOQ were calculated using the relationship LOD = (3.3 × standard deviation)/slope and LOQ = (10 × standard deviation)/slope. To calculate the relative standard deviation, the absorption measurements of ten blank samples were recorded. The calibration curves (absorbance vs. [Ag+]) were plotted (Fig. S6†), and then the obtained slope was used to calculate the LOD and LOQ. The obtained LOD and LOQ values of PTB-1 for Ag+ were found to be 3.67 μM and 0.11 μM, respectively.
:
H2O (20
:
80, v/v)] at 420 nm (λex = 290 nm) upon addition of Hg2+ ions (40 μL, 1 × 10−2 M, in H2O), while no significant changes were observed in the presence of other tested metal ions (Fig. 5A). The emission data of PTB-1 with Hg2+ exhibited an ≈23-fold fluorescence enhancement at 420 nm. In the fluorescence titration experiment (Fig. 5B), upon the addition of increasing amounts of Hg2+ ions from 0 to 40 μL (0–0.5 equivalent, 1 × 10−3 M, in H2O), the emission bands of PTB-1 at 420 nm increased dramatically, whereas less changes in the emission intensity were observed upon the addition of 80 μL (0–1 equivalent) and a decrease was observed after the addition of 1 equivalent (80 μL) of Hg2+ ions to 10 equivalents (800 μL). This suggested the formation of a host–guest complex of a 2
:
1 stoichiometry. To confirm this stoichiometry, the Job's plot analysis (Fig. S10†) and the mole ratio plot (Fig. S11†) were performed. More direct evidence for the formation of this 2
:
1 complex was evaluated from the ESI-MS spectra of PTB-1 in the presence and absence of 1.0 equivalent of Hg2+ in methanol/water (20
:
80, v/v) (Fig. S12†). The peaks at m/z = 715.0420 [{2(PTB-1)–2H + Hg} + H]+ and m/z = 258.0714 ([PTB-1 + H]+) corresponded to the complex and the receptor alone, respectively. Then, the binding constant (Ka) of PTB-1 with Hg2+ was determined by a Benesi–Hildebrand plot analysis by using the fluorescence titration data (Fig. S13†). The cation binding affinity of PTB-1 was found to be ≈100
000 M−1 for Hg2+. Based on the fluorescence titrations, the LOD and LOQ of PTB-1 for Hg2+ were found to be 0.69 nM and 0.02 nM, respectively, and these values are an improvement on reported sensors (Table S1†). Moreover, the linear response range of chemosensor PTB-1 was calculated by plotting the ratio of fluorescence intensity vs. the increasing concentration of Hg2+ and Ag+. The chemosensor exhibited a dynamic response range for Hg2+ (Fig. S14a†) from 1.0 × 10−7 to 1.8 × 10−5 M and 1.2 × 10−6 to 2.4 × 10−5 M for Ag+ (Fig. S14b†).
To examine the selectivity and reversibility of PTB-1 towards Ag+ and Hg2+, we carried out emission reversible titrations by using EDTA (Fig. S15†). Upon addition of an equimolar amount of EDTA solution [DMSO
:
H2O (90
:
10, v/v)] to the solution of PTB-1
:
Hg2+ [4 × 10−5 M, in CH3OH
:
H2O (20
:
80, v/v)], the color changed from yellow to colorless and a significant decrease in the fluorescence signal at 420 nm was observed (Fig. S15a†). These results indicate that PTB-1 detects Hg2+ ions reversibly. The sequential alternate addition of Hg2+ and EDTA solutions was repeated several times, which indicates only a slight decrease in the emission intensity, suggesting the reusability of PTB-1 (Fig. S15b†). In contrast, the alternate addition of an equimolar amount of Ag+ and EDTA solutions [DMSO
:
H2O (90
:
10, v/v)] to the solution of PTB-1
:
Ag+ [4 × 10−5 M, in CH3OH
:
H2O (20
:
80, v/v)] showed no change in color and fluorescence intensity (Fig. S15c and d†). These results indicate that the PTB-1
:
Ag+ complexation process was irreversible with EDTA.
![]() | ||
| Fig. 6 The DFT computed LUMO (above) and HOMO (below) diagrams of (a) PTB-1 and its (b) PTB-1·(Ag+)2 and (c) (PTB-1)2·Hg2+ complexes. | ||
Furthermore, we carried out 1H NMR spectroscopic titration experiments on PTB-1 solutions with various equivalents of Hg2+ and Ag+ ions separately (Fig. S17 and S18†). Upon addition of 0.5 equiv. of Hg2+ ions, it was observed that the peaks due to the two NH protons of PTB-1 at 13.12 and 9.07 ppm disappeared, whilst a broad peak appeared at 16.13 ppm probably due to the OH group (Fig. S17†). In addition, some of the aromatic protons of PTB-1 exhibited an up-field shift (from 8.83, 8.46 and 7.78 ppm to 8.46, 8.05 and 7.67 ppm, respectively) while some other aromatic protons exhibited a down-field shift (from 7.92, 7.54 and 7.18 to 8.06, 7.58 and 7.32 ppm, respectively) in the presence of Hg2+ ions accompanied by a broadening of the peaks. Similar NMR studies conducted on PTB-1 by adding various equivalents of Ag+ also exhibited the disappearance of both the NH protons of PTB-1 at 13.12 and 9.07 ppm (Fig. S18†); 2.0 equiv. of Ag+ ions are required for the complete disappearance of these peaks. However, in contrast to the case of Hg2+ addition, no broad peak at 16.12 ppm appeared upon addition of Ag+ ions. In addition, some of the aromatic protons of PTB-1 revealed an up-field shift (from 8.83 and 8.46 ppm to 8.37 and 8.06 ppm, respectively) whilst others exhibited a down-field shift (from 7.92, 7.54 and 7.18 ppm to 7.99, 7.59 and 7.51 ppm, respectively) upon addition of Ag+ ions, which was accompanied by broadening of peaks. It is noteworthy that some aromatic protons of PTB-1 experience a slight net increase in shielding which may be attributed to the anisotropic effect and conformation changes after coordination with Hg2+ or Ag+.33
Direct evidence for the formation of complexes of PTB-1 with Hg2+ and Ag+ was obtained from HR-MS analysis. The HR-MS spectra of pure PTB-1 exhibited a characteristic MS peak at m/z = 258.0714 corresponding to [(PTB-1) + H]+ (Fig. S4†). However, upon addition of 0.5 equivalents of the Hg2+ ion, a new peak appeared at m/z = 715.0420, corresponding to the species [{2(PTB-1) − 2H + Hg} + H]+, which confirmed the formation of a 2
:
1 complex of PTB-1 with the Hg2+ ion (Fig. S12†). Similarly, upon addition of 2.0 equivalents of Ag+, the parent ion peak of PTB-1 at m/z = 258.0714 disappeared and a new peak appeared at m/z = 491.2671 corresponding to the species [{(PTB-1) − 2H + 2Ag} + Na]+, suggesting the formation of a 1
:
2 complex (Fig. S8†). Additionally, FT-IR comparative studies of PTB-1 and the PTB-1·Hg2+ complex were performed (Fig. S19†). The shifting of the –NH, C
S and C
O bands also supports the proposed binding mechanism.
:
H2O (20
:
80, v/v)] and two equivalents of the other competitive metal ions (16 μL, 1 × 10−2 M, in H2O) of interest; their absorption and emission spectra were recorded. From the absorption study, the Ag+ selectivity of PTB-1 was not affected by the presence of the other tested ions, including Hg2+ (Fig. 7A). Similarly, the fluorescent sensing of Hg2+ by chemosensor PTB-1 was found to be barely affected by a number of commonly co-existing miscellaneous competitive cations, including Ag+ (Fig. 7B). Additionally, the UV-Vis and fluorescence responses of the sensor PTB-1 in acidic and basic pH regions were examined. It was observed that the optimum pH range for the use of PTB-1 for detecting Ag+ and Hg2+ ions was 5–9.
![]() | ||
| Fig. 7 Competitive (A) absorbance response of PTB-1 and PTB-1:Ag+ complex at 243 nm, (B) fluorescence response of PTB-1 and PTB-1:Hg2+ complex at 420 nm in presence of different metal cations. | ||
![]() | ||
| Fig. 8 Practical application of PTB-1 for the detection of Ag+ by (A) the test strip method and (B) the silica support method. | ||
The sensing of Ag+ by PTB-1 also worked on a solid support. The silica gel (60–120 mesh, 5.0 g, colorless) was soaked in PTB-1 (in methanol, 5 mL, 1 × 10−2 M) and then the solvent was removed. A very faint off-white color for the silica gel appeared, which indicated the adsorption of the receptor on the surface. When it was treated with 10 mL aqueous solution of Ag+ (1 × 10−4 M), the colorless solution promptly turned dark brown (Fig. 8B & ESI video†). The instantaneous color change of the solid silica gel in solution clearly inferred the practical application of PTB-1 for the qualitative detection of Ag+ in aqueous media.
:
H2O (20
:
80, v/v)] was also evaluated (Fig. S21†), and the fluorescence intensity hardly changed over 3 h. On this basis, we suggested that PTB-1 had good fluorescence stability.
To access the potential toxicity of PTB-1,34 MTT assays were carried out. HepG2 cells (106 cells per mL) were planted into 96-well microtiter plates in DMEM with 10% fetal bovine serum (FBS). Plates were maintained at 37 °C in a 5% CO2/95% air incubator for 12 h. Then the cells were incubated for 24 h at 37 °C in the 5% CO2/95% air incubator with different concentration probes of 0 μM to 100 μM, respectively. MTT solution (5.0 mg mL−1, PBS) was then added to each well. After 4 h, the remaining MTT solution was removed, and 200 μL of DMSO was added to each well, followed by shaking for 10 min to dissolve the formazan crystals at room temperature. Absorbance was measured at 490 nm using a TECAN infinite M200pro microplate reader. The high cell viability of PTB-1 indicated that the probe displayed low cytotoxicity to living cells (Fig. S22†).
S)–NH–C(
O)– is planar within 0.103(1) Å (Fig. 1). This conformation is stabilized by a short intramolecular hydrogen bond N(2)–H(2)⋯O(1) with an N⋯O separation of 2.592(2) Å. The phenyl ring C(12)–C(17) is slightly skewed around the C(11)–C(12) bond; the torsion angle O(1)–C(11)–C(12)–C(13) is equal to 25.6(3)°. According to the Cambridge Structural Database,32 all the bond lengths and angles in this structure exhibit ordinary values. In the structure, adjacent molecules are connected as centrosymmetric dimers via N(1)–H(1)⋯S(1) hydrogen bonds (Fig. S23†).
:
H2O (20
:
80, v/v) mixed solvents. For the spectroscopic (UV-Vis and fluorescence) titrations, the required amount of the diluted receptor PTB-1 [2 mL, 4 × 10−5 mol L−1, in CH3OH
:
H2O (20
:
80, v/v)] was taken directly into a cuvette and the spectra were recorded after each successive addition of cations (0–240 μL, 1 × 10−3 mol L−1, in H2O) by using a micropipette. The interaction of PTB-1 with Ag+ and Hg2+ ions was completed in less than 2 minutes, and therefore all readings were taken 2 minutes after the addition.
:
2 and 2
:
1 binding stoichiometry, respectively. Confocal microscopy images indicate that PTB-1 can be used for detecting changes in Hg2+ levels within living cells. Also, PTB-1 can be applied for the colorimetric detection of Ag+ in the aqueous media by the naked eye using test strip and silica support methods.
Footnotes |
| † Electronic supplementary information (ESI) available: Details about spectra and characterization data including IR, NMR, mass, crystallographic data and DFT data. CCDC 986043. For ESI and crystallographic data in CIF or other electronic format see DOI: 10.1039/c7dt02524f |
| ‡ CCDC 986043† contains the supplementary X-ray data for this paper. |
| This journal is © The Royal Society of Chemistry 2017 |