Location via proxy:   [ UP ]  
[Report a bug]   [Manage cookies]                
Next Article in Journal
Changes in Molecular Characteristics of Cereal Carbohydrates after Processing and Digestion
Next Article in Special Issue
Natural Biomolecules and Protein Aggregation: Emerging Strategies against Amyloidogenesis
Previous Article in Journal
Phase Transformations of α-Alumina Made from Waste Aluminum via a Precipitation Technique
Previous Article in Special Issue
Effects of Intramolecular Distance between Amyloidogenic Domains on Amyloid Aggregation
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Turn-On Fluorescent Chemosensor for Hg2+ Based on Multivalent Rhodamine Ligands

1
Laboratory of Molecular Nanofabrication, MESA+ Institute for Nanotechnology, University of Twente, Enschede 7500 AE, The Netherlands
2
Department of Chemistry and Material Engineering, Logistic Engineering University, Chongqing 401311, China
3
Department of Chemistry, University of Sargodha, Punjab 40100, Pakistan
*
Author to whom correspondence should be addressed.
Int. J. Mol. Sci. 2012, 13(12), 16822-16832; https://doi.org/10.3390/ijms131216822
Submission received: 22 November 2012 / Accepted: 4 December 2012 / Published: 7 December 2012
(This article belongs to the Special Issue Molecular Self-Assembly 2012)

Abstract

:
Rhodamine-based fluorescent chemosensors 1 and 2 exhibit selective fluorescence enhancement to Fe3+ and Hg2+ over other metal ions at 580 nm in CH3CN/H2O (3/1, v/v) solution. Bis(rhodamine) chemosensor 1, under optimized conditions (CH3CN/HEPES buffer (0.02 M, pH = 7.0) (95/5, v/v)), shows a high selectivity and sensitivity to Hg2+, with a linear working range of 0–50 μM, a wide pH span of 4–10, and a detection limit of 0.4 μM Hg2+.

1. Introduction

Mercury is considered to be a highly dangerous element by the United States Environmental Protection Agency due to its special properties, such as migration through cell membranes and bioaccumulation within living tissues [1,2]. Therefore, there is a high demand for the determination of the Hg2+ ion in environmental analysis.
In recent years, rhodamine-based fluorescent chemosensors have received considerable attention for the detection of Hg2+[314], Cu2+[1517], Pb2+[18], Cr3+[19], and Fe3+[20], because their special structural properties provide an ideal mode to construct off-on fluorescent switch chemosensors. Rhodamine having a spirolactam structure is non-fluorescent, whereas ring-opening of the spirolactam gives rise to a strong fluorescence emission. Moreover, they have a longer emission wavelength (about 550 nm), which is often preferred to serve as reporting group for analytes to avoid the influence of the background fluorescence (below 500 nm) [2123]. However, most of them have shortcomings in practical application, such as cross-sensitivities toward other metal cations, low water solubility, a narrow pH span, and delayed response, etc. Accordingly, quantitative practical Hg2+ detection requires a linear fluorescence response, uniform fluorescence output at a broad pH range, compatibility with aqueous medium, high selectivity, sensitivity, and a fast response, while easy synthetic procedures for the sensors are of utmost importance.
This study deals with new rhodamine-based CHEF (chelation-enhanced fluorescence) chemosensors 1 and 2 (Chart 1) for the detection of Hg2+ ions showing that, compared to related rhodamine-based chemosensors, small structural changes give rise to improved selectivity and sensitivity. Chemosensor 1 is a bis(rhodamine) in which the two units are connected via amide groups meta substituted to a benzene ring. In order to study the influence of a third functionalized rhodamine on the Hg2+ complexation, tris(rhodamine) chemosensor 2 was prepared and evaluated for comparison.

2. Results and Discussion

Rhodamine derivatives 1 and 2, possessing two or three rhodamine moieties, respectively, were prepared by reacting rhodamine B hydrazide (4) with isophthaloyl dichloride (3) or benzene-1,3,5-tricarbonyl trichloride (5) in THF as a solvent (Scheme 1). The formation of 1 and 2 followed from the 1H NMR spectra as the doublets at 6.42 and 6.46 ppm in rhodamine B hydrazide (4) shifted to 6.61–6.75 ppm and 6.59–6.76 ppm as multiplets for 1 and 2, respectively. In the ESI-MS mass spectra the [M+H] peaks were found at m/z 1043.5 and 1525.7 for 1 and 2, respectively.
The perchlorate salts of Na+, K+, Pb2+, Co2+, Cd2+, Cs+, Ag+, Cu2+, Mg2+, Zn2+, Hg2+, Fe2+, and Fe3+ ions were used to evaluate the metal ion binding properties of chemosensors 1 and 2 in CH3CN/H2O (3/1, v/v). The fluorescence spectra were obtained by excitation of the rhodamine fluorophore at 510 nm. Among these metal ions (80 equiv), chemosensors 1 and 2 both showed large chelation enhanced fluorescence (CHEF) effects with Hg2+, Fe3+ and smaller CHEF effects with Cu2+ (Figure 1). The addition of 400 μM (80 equiv) of Fe3+ and Hg2+ immediately yielded a pink solution with a absorption signal at 561 nm [24] and a strong fluorescence signal at 580 and 590 nm, respectively (Figure 2). For chemosensor 1, there was 35-fold enhancement with Fe3+ and 84-fold enhancement with Hg2+, while chemosensor 2 yielded a 27-fold enhancement with Fe3+ and 33-fold with Hg2+. The results can be attributed to a similar binding behavior of 1 and 2 both containing rhodamine moieties. In addition, a very weak fluorescence signal for free 1 and 2 was observed at 580 and 590 nm, respectively, upon excitation at 510 nm, confirming the presence of a ring-closed spirolactam structure, whereas with the addition of Fe3+ or Hg2+ ions, ring-opening of the spirolactam occurs and gives rise to a strong fluorescence emission at 580 and 590 nm, respectively. Though Cu2+ gave a small color change and a very small fluorescence enhancement, the spectroscopy and interaction of chemosensors 1 and 2 with Cu2+ are completely different from those of 1 and 2 with Fe3+ and Hg2+ as recently reported by others [20].
To investigate the binding mode and the affinity, Job’s plots (see Figure S1) were determined and fluorescence titration experiments were carried out for chemosensors 1 and 2 with Fe3+ and Hg2+ (Figure 3). The Job’s plots show that in all cases 1:1 complexes were formed. The resulting titrations also fitted to a 1:1 binding model, and the association constant (Ks) can be gained using Equation 1 [25,26].
( I - I 0 ) I 0 = α × [ M ] ( 1 / K s ) + [ M ]
Where I0 is the fluorescence intensity of the chemosensors 1 and 2 in the absence of metal ions and I is the fluorescence intensity upon the addition of metal ions. α is the maximum specific binding, [M] is the metal ion concentration, Ks is the association constant.
The association constants for 1 with Fe3+ and Hg2+ were found to be 7.99 × 103 M−1 and 8.62 × 103 M−1, while those for 2 with Fe3+ and Hg2+ were 6.18 × 103 M−1 and 6.08 × 103 M−1, respectively, which are close to those of a related bis(rhodamine) chemosensor [20]. The Ks values of chemosensors 1 and 2 only marginally differ, those of tris(rhodamine) 2 even being slightly smaller than those of bis(rhodamine) 1. In addition to the Job’s plot determination, this also demonstrates that two rhodamines are sufficient for optimal metal ion binding. In chemosensor 1, two carbonyl oxygens as well as two amide oxygens can provide a stable binding pocket for metal ions.
To obtain a high selectivity and sensitivity for Hg2+ under aqueous conditions, HEPES buffer (0.02 M, pH = 7.0), MES buffer (0.01 M, pH = 7.0), PES buffer (0.01 M, pH = 7.0), and Tris HCl buffer (0.01 M, pH = 7.0) were used, respectively (Figure 4a). The fluorescence intensities upon addition of 40 equiv of Fe3+, Hg2+, and Cu2+ ions show the effect of the different buffer systems. In this case, HEPES effectively inhibits the interference of Fe3+ and Cu2+ ions during the detection of Hg2+.
The fraction of HEPES buffer used in CH3CN played an important role in the affinity of 1 toward Hg2+. Because of the strong interaction between buffer anions and Fe3+, a small fraction of HEPES buffer in organic solvent was already beneficial to inhibit the binding of Fe3+. However, a high fraction of HEPES buffer caused a decrease of the fluorescence emission for 1·Hg2+ and an increase of that of the complex with Cu2+, which has to be avoided for Hg2+ analysis. To determine the optimal analysis condition, 5 μM chemosensor 1 in CH3CN containing different fractions (5%, 10%, 15%, and 25% (v/v)) of 0.02 M HEPES buffer at pH 7.0 were used for the detection of Fe3+, Hg2+, and Cu2+ (Figure 4b). No significant fluorescence enhancement could be observed at 580 nm for Fe3+ compared to that of Hg2+ and Cu2+ at the same concentration. The results already show that 5% HEPES/CH3CN was already sufficient for efficient monitoring of Hg2+.
Fluorescence titrations of Hg2+ by 1 were performed, under the optimized conditions of CH3CN/HEPES buffer (0.02 M, pH = 7.0) (95/5, v/v) (Figure 5). For the quantitative detection of Hg2+ ions, under the optimized conditions, a calibration curve was generated by determining the fluorescence intensity of 1 (5 μM) at 580 nm upon addition of Hg2+ ions with different concentrations, ranging from 0 to 50 μM [27]. Figure 5 exhibits over the entire Hg2+ concentration range an almost perfect linearity (I580 = 1.43 × [Hg2+] + 9.34, R2 = 0.9962) between the fluorescence intensity of 1 and the Hg2+ concentration, indicating a linear detection range for Hg2+ determination. The detection limit, defined as three times the standard deviation of the blank signals [28], was found to be 0.4 μM from 10 blank solutions. In addition, Figure 6 shows that chemosensor 1 detected Hg2+ ions with high selectivity under these conditions.
For practical applicability of this new chemosensor, a proper pH range of 4–10 was determined. Figure 7a shows variations of the fluorescence intensity of 1 with pH in the absence and presence of the Hg2+ ion in CH3CN/H2O solution (95/5, v/v). In this region, free 1 has a weak fluorescence emission due to the presence of the ring-closed spirolactam structure, while addition of the Hg2+ ion leads to ring-opening of the spirolactam ring, resulting in a remarkable increase of the fluorescence.
The ring-opening of the spirolactam in chemosensor 1 produced a time-dependent dosimetric response, controlled by the reaction kinetics. Under the optimized conditions less than 4 min were required to complete the reaction (Figure 7b).
Chemosensor 1 in CH3CN/HEPES buffer (0.02 M, pH = 7.0) (95/5, v/v) has a low detection limit (0.4 μM), a large linear detection range (0–50 μM), a wide pH span (4–10), and a rapid response time (4 min), exhibiting higher sensitivity and selectivity than most other previously reported rhodamine-based chemosensors [314].

3. Experimental Section

3.1. General

Absolute acetonitrile of analytical grade and deionized water were used throughout the experiments. All chemicals needed for the synthesis were purchased from known suppliers and used without further purification. The known rhodamine B hydrazide (4) was prepared according to a literature procedure [29]. The metal ion solutions were prepared from their analytical grade perchlorate salts. HEPES buffer, MES buffer, PES buffer, Tris HCl buffer solutions and different pH solutions were prepared using proper amounts of HEPES, MES, PES, Tris, 1.0 M HCl, and 1.0 M NaOH (all of analytical grade) under adjustment by a pH meter.

3.2. Equipment

Absorption spectra were determined on a Perkin Elmer Lambda 850 UV-vis spectrophotometer. Fluorescence spectroscopy measurements were performed on a Perkin Elmer LS55 spectrofluorimeter equipped with a xenon discharge lamp and using 1 cm quartz cells. All pH measurements were made with a Mettler Toledo SevenEasy pH meter. 1H NMR and 13C NMR spectra were recorded on a Varian Unity INOVA (300 MHz) spectrometer in CDCl3. 1H NMR (300 MHz) and 13C NMR (75 MHz) chemical shift values are reported as δ using the residual solvent signal as an internal standard. Electrospray Ionization (positive mode) mass spectra were recorded on a WATERS LCT mass spectrometer.

3.3. Synthesis of 1 and 2

3.3.1. General Procedure for the Synthesis of 1 and 2

To a solution of rhodamine B hydrazide (4) and triethylamine in THF a solution of isophthaloyl dichloride (3) or benzene-1,3,5-tricarbonyl trichloride (5) in THF was added dropwise at 0 °C. The reaction mixture was brought to room temperature in 1 h, followed by stirring overnight at room temperature. The solvent was evaporated and the residue was dissolved in dichloromethane (50 mL), washed with 10% NaHCO3 solution (3 × 50 mL) and water (3 × 50 mL). The organic layer was concentrated under reduced pressure to afford crude products 1 or 2.
Chemosensor 1 was synthesized starting from rhodamine B hydrazide (4) (1.3 g, 2.8 mmol), isophthaloyl dichloride (3) (0.29 g, 1.4 mmol) in THF (5 mL) and triethylamine (0.3 g, 3.0 mmol) in THF (70 mL). The crude product was recrystallized from a mixture of diethyl ether and dichloromethane (3:1) to afford the pure product (0.77 g, 52%) as a solid. mp 184 °C–186 °C. 1H NMR: δ 1.02–1.22 (m, 24H, CH3), 3.17–3.41 (m, 16H, CH2), 6.22–6.40 (m, 8H, ArH), 6.61–6.75 (m, 4H, ArH). 7.15 (d, J = 6.0 Hz, 2H, ArH), 7.39–7.47 (m, 2H, ArH), 7.47–7.56 (m, 4H, ArH), 7.61–7.69 (m, 2H, ArH), 7.96 (d, J = 6.0 Hz, 2H, ArH). 13C NMR: δ 12.6, 44.3, 97.7, 98.0, 107.9, 123.5, 124.2, 128.3, 129.3, 131.0, 133.1, 149.0, 153.7. ESI MS: m/z 1043.6, calculated: 1043.5 for [M+H]+.
Chemosensor 2 was prepared starting from rhodamine B hydrazide (4) (1.5 g, 3.3 mmol), benzene-1,3,5-tricarbonyl trichloride (5) (0.28 g, 1.1 mmol) in THF (5 mL) and triethylamine (0.35 g, 3.5 mmol) in THF (70 mL). The crude product was recrystallized from a mixture of diethyl ether and dichloromethane (3:1) to afford the pure product (1.02 g, 61%) as a solid. mp 204 °C–206 °C. 1H NMR: δ 1.05–1.24 (m, 36H, CH3), 3.19–3.39 (m, 24H, CH2), 6.21–6.41(m, 12H, ArH), 6.59–6.76 (m, 6H, ArH), 7.12 (d, J = 6.0 Hz, 3H, ArH), 7.38–7.56 (m, 6H, ArH), 7.88–8.01 (m, 6H, ArH). 13C NMR: δ 12.6, 44.2, 98.0, 99.9, 103.9, 107.9, 123.5, 124.2, 127.9, 129.2, 129.8, 132.9, 149.0, 153.6. ESI MS: m/z 1525.7, calculated: 1525.7 for [M+H]+.

3.4. Absorption and Fluorescence Measurements

Absorption and fluorescence titrations were performed in a 1 cm quartz cell by addition of small aliquots of metal ion work solutions to a 3 mL solution of proper amounts of 1 and 2 in CH3CN/H2O (3/1, v/v) and a 3 mL solution of a proper amount of 1 in CH3CN/HEPES buffer (0.02 M, pH = 7.0) (95/5, v/v). After thorough mixing, the solutions were allowed to stand at ambient temperature for 5 min, whereupon absorption or fluorescence spectra were recorded. Both the excitation and emission slits were 5 nm.
To determine the optimal conditions for Hg2+ detection, small aliquots of Hg2+, Cu2+, and Fe3+ work solutions were respectively added into 5 μM chemosensor 1 solutions which contained different fractions (5%, 10%, 15%, and 20%) of HEPES buffer (0.02 M, pH = 7.0) in CH3CN and mixed in a 1 cm quartz cell for 5 min. Then the fluorescence measurement was performed at ex/em = 510/580 nm.

4. Conclusions

In conclusion, the rhodamine derivatives 1 and 2 are very good fluorescent chemosensors, with a good selectivity toward Hg2+ and Fe3+ over other competitive ions in CH3CN/H2O (3/1, v/v). For practical Hg2+ detection, the experimental conditions were optimized to CH3CN/HEPES buffer (0.02 M, pH = 7.0) (95/5, v/v). Under these conditions, the fluorimetric quantification of Hg2+ by 1 was satisfactory in a linear working range of 0–50 μM, with a detection limit of 0.4 μM Hg2+ and a pH span of 4–10. These very good features make chemosensor 1 very promising for practical applications.

Supplementary Information

ijms-13-16822-s001.pdf

Acknowledgments

The authors would like to thank Hua Yan and acknowledge the support of the Logistic Engineering University in China.
  • Conflict of InterestThe authors declare no conflict of interest.

References and Notes

  1. Miller, J.R.; Rowland, J.; Lechler, P.J.; Desilets, M.; Hsu, L.C. Dispersal of mercury-contaminated sediments by geomorphic processes, Sixmile Canyon, Nevada, USA: Implications to site characterization and remediation of fluvial environments. Water Air Soil Pollut 1996, 86, 373–388. [Google Scholar]
  2. Tchounwou, P.B.; Ayensu, W.K.; Ninashvili, N.; Sutton, D. Environmental exposure to mercury and its toxicopathologic implications for public health. Environ. Toxicol 2003, 18, 149–175. [Google Scholar]
  3. Zhan, X.-Q.; Qian, Z.-H.; Zheng, H.; Su, B.-Y.; Lan, Z.; Xu, J.-G. Rhodamine thiospirolactone. Highly selective and sensitive reversible sensing of Hg(II). Chem. Commun. 2008, 1859–1861. [Google Scholar]
  4. Huang, J.; Xu, Y.; Qian, X. A rhodamine-based Hg2+ sensor with high selectivity and sensitivity in aqueous solution: A NS2-containing receptor. J. Org. Chem 2009, 74, 2167–2170. [Google Scholar]
  5. Wu, J.-S.; Hwang, I.-C.; Kim, K.S.; Kim, J.S. Rhodamine-based Hg2+ selective chemodosimeter in aqueous solution: Fluorescent off-on. Org. Lett 2007, 9, 907–910. [Google Scholar]
  6. Zheng, H.; Qian, Z.-H.; Xu, L.; Yuan, F.-F.; Lan, L.-D.; Xu, J.-G. Switching the recognition preference of rhodamine B spirolactam by replacing one atom: Design of rhodamine B thiohydrazide for recognition of Hg2+ in aqueous solution. Org. Lett 2006, 8, 859–861. [Google Scholar]
  7. Lee, M.H.; Wu, J.-S.; Lee, J.W.; Jung, J.H.; Kim, J.S. Highly sensitive and selective chemosensor for Hg2+ based on the rhodamine fluorophore. Org. Lett 2007, 9, 2501–2504. [Google Scholar]
  8. Ko, S.-K.; Yang, Y.-K.; Tae, J.; Shin, I. In vivo monitoring of mercury ions using a rhodamine-based molecular probe. J. Am. Chem. Soc 2006, 128, 14150–14155. [Google Scholar]
  9. Yang, H.; Zhou, Z.; Huang, K.; Yu, M.; Li, F.; Yi, T.; Huang, C. Multisignaling optical-electrochemical sensor for Hg2+ based on a rhodamine derivative with a ferrocene unit. Org. Lett 2007, 9, 4729–4732. [Google Scholar]
  10. Soh, J.H.; Swamy, K.M.K.; Kim, S.K.; Kim, S.; Lee, S.H.; Yoon, J. Rhodamine urea derivatives as fluorescent chemosensors for Hg2+. Tetrahedron Lett 2007, 48, 5966–5969. [Google Scholar]
  11. Huang, W.; Song, C.; He, C.; Lv, G.; Hu, X.; Zhu, X.; Duan, C. Recognition preference of rhodamine-thiospirolactams for mercury(II) in aqueous solution. Inorg. Chem 2009, 48, 5061–5072. [Google Scholar]
  12. Chen, X.; Nam, S.-W.; Jou, M.J.; Kim, Y.; Kim, S.-J.; Park, S.; Yoon, J. Hg2+ selective fluorescent and colorimetric sensor: Its crystal structure and application to bioimaging. Org. Lett 2008, 10, 5235–5238. [Google Scholar]
  13. Rode, A.B.; Kim, J.; Kim, S.-H.; Gupta, G.; Hong, I.S. A highly selective chemodosimeter for the rapid detection of Hg2+ ions in aqueous media. Tetrahedron Lett 2012, 53, 2571–2574. [Google Scholar]
  14. Han, R.; Yang, X.; Zhang, D.; Fan, M.; Ye, Y.; Zhao, Y. A bis(rhodamine)-based highly sensitive and selective fluorescent chemosensor for Hg(II) in aqueous media. New J. Chem 2012, 36, 1961–1965. [Google Scholar]
  15. Xiang, Y.; Tong, A.; Jin, P.; Ju, Y. New fluorescent rhodamine hydrazone chemosensor for Cu(II) with high selectivity and sensitivity. Org. Lett 2006, 8, 2863–2866. [Google Scholar]
  16. Duan, Y.L.; Shi, Y.G.; Chen, J.H.; Wu, X.H.; Wang, G.K.; Zhou, Y.; Zhang, J.F. 1,8-Naphthyridine modified rhodamine B derivative and Cu2+ complex: Colorimetric sensing of thiols in aqueous media. Tetrahedron Lett 2012, 53, 6544–6547. [Google Scholar]
  17. Kim, Y.-R.; Kim, H.J.; Kim, J.S.; Kim, H. Rhodamine-based “turn-on” fluorescent chemodosimeter for Cu(II) on ultrathin platinum films as molecular switches. Adv. Mater 2008, 20, 4428–4432. [Google Scholar]
  18. Kwon, J.Y.; Jang, Y.J.; Lee, Y.J.; Kim, K.M.; Seo, M.S.; Nam, W.; Yoon, J. A highly selective fluorescent chemosensor for Pb2+. J. Am. Chem. Soc 2005, 127, 10107–10111. [Google Scholar]
  19. Weerasinghe, A.J.; Schmiesing, C.; Sinn, E. Highly sensitive and selective reversible sensor for the detection of Cr3+. Tetrahedron Lett 2009, 50, 6407–6410. [Google Scholar]
  20. Weerasinghe, A.J.; Schmiesing, C.; Varaganti, S.; Ramakrishna, G.; Sinn, E. Single- and multiphoton turn-on fluorescent Fe3+ sensors based on bis(rhodamine). J. Phys. Chem. B 2010, 114, 9413–9419. [Google Scholar]
  21. Chen, X.; Pradhan, T.; Wang, F.; Kim, J.S.; Yoon, J. Fluorescent chemosensors based on spiroring-opening of xanthenes and related derivatives. Chem. Rev 2012, 112, 1910–1956. [Google Scholar]
  22. Kim, H.N.; Lee, M.H.; Kim, H.J.; Kim, J.S.; Yoon, J. A new trend in rhodamine-based chemosensors: Application of spirolactam ring-opening to sensing ions. Chem. Soc. Rev. 2008, 37, 1465–1472. [Google Scholar]
  23. Zhang, J.F.; Kim, J.S. Small-molecule fluorescent chemosensors for Hg2+ ion. Jpn. Soc. Anal. Chem 2009, 25, 1271–1281. [Google Scholar]
  24. The Fe3+ complexes show a huge absorbance at short wavelength probably due to scattering.
  25. Connors, K.A. Binding Constants: The Measurement of Molecular Complex Stability; Wiley-Interscience: New York, NY, USA, 1987; pp. 59–65. [Google Scholar]
  26. Valeur, B. Molecular Fluorescence: Principles and Applications; Wiley-VCH: New York, NY, USA, 2002; p. 339. [Google Scholar]
  27. Ks cannot be determined in this Hg2+ concentration range.
  28. Skoog, D.A.; Holler, F.J.; Nieman, A. Principles of Instrumental Analysis, 5th ed; Saunders: New York, NY, USA, 2000; pp. 20–21. [Google Scholar]
  29. Yang, X.-F.; Guo, X.-Q.; Zhao, Y.-B. Novel spectrofluorimetric method for the determination of sulfite with rhodamine B hydrazide in a micellar medium. Anal. Chim. Acta 2002, 456, 121–128. [Google Scholar]
Figure 1. Fluorescence (left) and absorption (right) spectra of 1 (a) and 2 (b) (5 μM) in CH3CN/H2O (3/1, v/v) with different metal ions (400 μM), respectively.
Figure 1. Fluorescence (left) and absorption (right) spectra of 1 (a) and 2 (b) (5 μM) in CH3CN/H2O (3/1, v/v) with different metal ions (400 μM), respectively.
Ijms 13 16822f1
Figure 2. Photos of chemosensor 1 (5 μM) in CH3CN/H2O (3/1, v/v) upon addition of 80 equiv of Cu2+, Fe3+, and Hg2+ ions, respectively.
Figure 2. Photos of chemosensor 1 (5 μM) in CH3CN/H2O (3/1, v/v) upon addition of 80 equiv of Cu2+, Fe3+, and Hg2+ ions, respectively.
Ijms 13 16822f2
Figure 3. Changes of the fluorescence spectra of (a) chemosensor 1 and (b) chemosensor 2 (5 μM, λex = 510 nm) in CH3CN/H2O (3/1, v/v) upon addition of increasing amounts of Fe3+ (0–370 μM, left) and Hg2+ (0–400 μM, right), respectively. Inset: Spectrofluorimetric titration curves ((a) λem =580 nm and (b) λem = 590 nm) for a 1:1 complex according to Equation 1. The data are fitted to a curve with a correlation coefficient of (a) R2 = 0.9952, R2 = 0.9972 and (b) R2 = 0.9945, R2 = 0.9983.
Figure 3. Changes of the fluorescence spectra of (a) chemosensor 1 and (b) chemosensor 2 (5 μM, λex = 510 nm) in CH3CN/H2O (3/1, v/v) upon addition of increasing amounts of Fe3+ (0–370 μM, left) and Hg2+ (0–400 μM, right), respectively. Inset: Spectrofluorimetric titration curves ((a) λem =580 nm and (b) λem = 590 nm) for a 1:1 complex according to Equation 1. The data are fitted to a curve with a correlation coefficient of (a) R2 = 0.9952, R2 = 0.9972 and (b) R2 = 0.9945, R2 = 0.9983.
Ijms 13 16822f3
Figure 4. Fluorescence response of chemosensor 1 (5.0 μM, λex = 510 nm and λem = 580 nm) (a) in CH3CN/buffer (pH = 7.0) (95/5, v/v) upon addition of 40 equiv of Fe3+, Hg2+, and Cu2+ ions, respectively, and (b) in different fractions of HEPES buffer (0.02 M, pH = 7.0) upon addition of 40 equiv of Fe3+, Hg2+, and Cu2+ ions, respectively. The responses for Fe3+ are below 0.05 in the different fractions of HEPES buffer.
Figure 4. Fluorescence response of chemosensor 1 (5.0 μM, λex = 510 nm and λem = 580 nm) (a) in CH3CN/buffer (pH = 7.0) (95/5, v/v) upon addition of 40 equiv of Fe3+, Hg2+, and Cu2+ ions, respectively, and (b) in different fractions of HEPES buffer (0.02 M, pH = 7.0) upon addition of 40 equiv of Fe3+, Hg2+, and Cu2+ ions, respectively. The responses for Fe3+ are below 0.05 in the different fractions of HEPES buffer.
Ijms 13 16822f4
Figure 5. Changes of the fluorescence spectra of chemosensor 1 (5 μM, λex = 510 nm) in CH3CN/HEPES buffer (0.02 M, pH = 7.0) (95/5, v/v) upon addition of increasing amounts of Hg2+ (0–50 μM). Inset: Fluorescence intensity of 1 at 580 nm (5 μM, λex = 510 nm) in CH3CN/HEPES buffer (0.02 M, pH = 7.0) (95/5, v/v) vs the concentration of Hg2+ ions.
Figure 5. Changes of the fluorescence spectra of chemosensor 1 (5 μM, λex = 510 nm) in CH3CN/HEPES buffer (0.02 M, pH = 7.0) (95/5, v/v) upon addition of increasing amounts of Hg2+ (0–50 μM). Inset: Fluorescence intensity of 1 at 580 nm (5 μM, λex = 510 nm) in CH3CN/HEPES buffer (0.02 M, pH = 7.0) (95/5, v/v) vs the concentration of Hg2+ ions.
Ijms 13 16822f5
Figure 6. Bar profiles of fluorescence intensity for chemosensor 1 (5 μM, λex = 510 nm) in CH3CN/HEPES (95/5, v/v) upon addition of 10 equiv of various metal ions as perchlorates.
Figure 6. Bar profiles of fluorescence intensity for chemosensor 1 (5 μM, λex = 510 nm) in CH3CN/HEPES (95/5, v/v) upon addition of 10 equiv of various metal ions as perchlorates.
Ijms 13 16822f6
Figure 7. Fluorescence intensity of 1 at 580 nm (5 μM, λex = 510 nm) in CH3CN/H2O (95/5, v/v) (a) with and without Hg2+ ion (50 μM) as a function of pH and (b) upon addition of Hg2+ ion (50 μM) over time.
Figure 7. Fluorescence intensity of 1 at 580 nm (5 μM, λex = 510 nm) in CH3CN/H2O (95/5, v/v) (a) with and without Hg2+ ion (50 μM) as a function of pH and (b) upon addition of Hg2+ ion (50 μM) over time.
Ijms 13 16822f7
Scheme 1. Synthesis of chemosensors 1 and 2.
Scheme 1. Synthesis of chemosensors 1 and 2.
Ijms 13 16822f8
Chart 1. Structure of chemosensors 1 and 2.
Chart 1. Structure of chemosensors 1 and 2.
Ijms 13 16822f9

Share and Cite

MDPI and ACS Style

Wang, X.; Iqbal, M.; Huskens, J.; Verboom, W. Turn-On Fluorescent Chemosensor for Hg2+ Based on Multivalent Rhodamine Ligands. Int. J. Mol. Sci. 2012, 13, 16822-16832. https://doi.org/10.3390/ijms131216822

AMA Style

Wang X, Iqbal M, Huskens J, Verboom W. Turn-On Fluorescent Chemosensor for Hg2+ Based on Multivalent Rhodamine Ligands. International Journal of Molecular Sciences. 2012; 13(12):16822-16832. https://doi.org/10.3390/ijms131216822

Chicago/Turabian Style

Wang, Xuemei, Mudassir Iqbal, Jurriaan Huskens, and Willem Verboom. 2012. "Turn-On Fluorescent Chemosensor for Hg2+ Based on Multivalent Rhodamine Ligands" International Journal of Molecular Sciences 13, no. 12: 16822-16832. https://doi.org/10.3390/ijms131216822

Article Metrics

Back to TopTop