A new fluorescent chemosensor for Pb2+ ions based on naphthalene derivatives

A new fluorescent chemosensor for Pb2+ ions based on naphthalene derivatives

Accepted Manuscript A new fluorescent chemosensor for Pb2+ ions based on naphthalene derivatives Reza Azadbakht, Hojat Vaisi, Hossain Mohamadvand, Jav...

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Accepted Manuscript A new fluorescent chemosensor for Pb2+ ions based on naphthalene derivatives Reza Azadbakht, Hojat Vaisi, Hossain Mohamadvand, Javad Khanabadi PII: DOI: Reference:

S1386-1425(15)00314-5 http://dx.doi.org/10.1016/j.saa.2015.03.018 SAA 13432

To appear in:

Spectrochimica Acta Part A: Molecular and Biomolecular Spectroscopy

Received Date: Revised Date: Accepted Date:

26 October 2014 10 February 2015 1 March 2015

Please cite this article as: R. Azadbakht, H. Vaisi, H. Mohamadvand, J. Khanabadi, A new fluorescent chemosensor for Pb2+ ions based on naphthalene derivatives, Spectrochimica Acta Part A: Molecular and Biomolecular Spectroscopy (2015), doi: http://dx.doi.org/10.1016/j.saa.2015.03.018

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A new fluorescent chemosensor for Pb2+ ions based on naphthalene derivatives Reza Azadbakht*, Hojat Vaisi, Hossain Mohamadvand, Javad Khanabadi Department of chemistry, Payame Noor Universtiy, P.O. Box 19395-3697, Iran

Abstract A new naphthalene derivative receptor (L) was synthesized and characterized with common spectroscopic methods. L exhibited a strong fluorescence enhancement in the presence of trace amounts of Pb2+, attributable to photoinduced electron transfer (PET) effect, which also displayed high selectivity over a series of other metal cations (Na+, K+, Cs+, Mg2+, Ba2+, Cr3+, Mn2+, Fe3+, Fe2+, Co2+, Ni2+, Cu2+, Zn2+, Cd2+, Hg2+ and Ag+ ) in acetonitrile/H2O (9:1, v/v) mixture. Keywords: Fluorescence, Chemosensor, Pb2+ ion, Naphthalene.

1. Introduction Heavy metal pollution is a serious environmental problem of global concern. Among these toxic metal ions, Pb2+ is one of the oldest known and most widely studied toxins [1]. Lead widely exists in various forms including elemental, inorganic and organic compounds. Lead compounds are used in construction materials for tank linings, piping, equipment for handling corrosive gases and liquids used in petroleum refining, halogenation, sulfonation, extraction, condensation, metallurgy, and for pigments for paints. It is also used in ceramics, plastics, electronic devices, as a component of lead batteries, and in the production of ammunition, solder, cable covering, and sheet lead. Moreover, lead also remains in trace amount in soil, water and food [2]. In babies and children, exposure to lead in drinking water above the action level can result in delays in physical and mental development, along with *Corresponding author. Tel.: +98 8125221144; fax: +98 8112546840. E-mail address: [email protected] (R. Azadbakht).

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slight deficits in attention span and learning abilities. In adults, lead can increase blood pressure and cause fertility problems, nerve disorders, muscle and joint pain, irritability, and memory or concentration problems [3-8]. Thus, the concentration of lead in environment should be kept under permanent control. Although some atomic absorption spectroscopy techniques such as ICP-MS and ICP-AES can complete the quantitative analysis of the total amount of Pb2+ ion in the system [9–11], some inherent limitations such as complicated program, high initial cost, costly maintenance and consumables make the usage of these techniques became uneasily accessible. Thus, it is urgent to develop a convenient, sensitive and inexpensive method to detect trace level of Pb2+ ion. In recent years, fluorescence chemosensors have rapidly developed because of their miniature constitution, low cost manufacture, reusability, high selectivity and real-time measurement. Herein, we report the synthesis and properties of a highly turn-on lead fluorescent sensor (L) that binds Pb2+ with high affinity and displays selectivity against other physiological metals in aqueous media. In the presence of Pb2+, L exhibits significant fluorescence enhancements owing to PET (photoinduced electron transfer).

2. Experimental 2.1. Materials and instruments All solvents were of reagent grade quality and purchased commercially. 2-aminophenol was obtained

from

Merck

and

was

used

without

further

purification.

2-[2-(2-

formylnaphthoxy)ethoxy]naphthaldehyde was synthesized according to the literature method [12]. NMR spectra were obtained using a Bruker A V300 MHz spectrometer. Infrared spectra were recorded in KBr pellets using a BIO-RAD FTS-40A spectrophotometer (4000–400 cm1

). Positive ion FAB mass spectra were recorded on a Kratos-MS-50 spectrometer with 3-

nitrobenzyl alcohol as the matrix solvent. Uv–Vis absorption spectra were obtained on a

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Varian Cary Eclipse 300 spectrophotometer. The fluorescence spectra were recorded on a Varian spectrofluorometer. Both excitation and emission bands were set at 5 nm.

2.2. Synthesis of L A solution of 2-aminoethanol (0.12 g, 2 mmol) in absolute methanol (25 mL) was added dropwise to a hot solution of 2-[2-(2-formylnaphthoxy)ethoxy]naphthaldehyde (0.374, 1 mmol) in absolute methanol (50 mL). The solution was gently refluxed for 6 h. The solution was then allowed to cool to room temperature after which sodium borohydride (1 g, 26 mmol) was added in small portions to the stirred solution over 10 min. Excess water was added to the solution and the pH was adjusted to 12 with potassium hydroxide. The solution was extracted with chloroform (×3). The chloroform extracts were combined and dried over anhydrous sodium sulfate. The dried extracts were then reduced to a small volume on a rotary evaporator. A precipitate was obtained by standing overnight at 0 ºC. Yield (75%). Anal. Calc. for C28H32N2O4: C, 73.02; H, 7.00; N, 6.08. Found: C, 72.98; H, 7.13; N, 6.14 %. IR (KBr,cm-1) 3303 and 1623(NH starching and bending), 3387 (OH); 1HNMR δH (CDCl3, ppm) 2.64 (t, 4H), 3.59 (t, 4H), 4.36 (s, 4H), 4.59 (s, 4H), 7.38 (m, 4H), 7.54 (m, 2H), 7.84 (m, 4H), 8.04 (d, 2H); 13C NMR δC (CDCl3, ppm) 42.82, 50.83, 60.65, 67.78, 113.43, 121.23, 122.87, 123.75, 123.94, 124.10, 127.04, 128.68, 129.17,129.41, 133.39, 154.10. The mass spectrum show peak at m/z = 460 corresponding to L (S. 1).

2. 3. Theoretical calculations

The complex of [PbL]2+ gave fine powders and we were not able to prepare single crystals for structure determination by X-ray spectroscopy. Instead, The geometry of [PbL]2+ was fully optimized at DFT [13,14] levels of theory using the GAUSSIAN 03 program [15]. A starting semiempirical structure was optimized using the HYPERCHEM 5.02 series of programs [16].

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3. Results and discussion 3.1. Synthesis and characterization of L Synthesis of L can be achieved very easily in 75% yield by schiff base condensation of 2-[2(2-formylnaphthoxy)ethoxy]naphthaldehyde [12] with 2-aminoethanol in methanol, followed by reduction with NaBH4 (S. 2). L was characterized by microanalysis, mass spectrometry, IR, and NMR studies. L was soluble in polar solvents, such as chloroform and methanol and was hydrolytically stable under both basic and acidic conditions. The reduction of the imine groups was indicated in the IR spectrum, by the appearance of weak bands related to N-H in the region of 3303 cm-1, while no bands attributable to C=N were detected. Two absorption bands in the 2919 cm-1 and 2928 are attributed to the asymmetric and symmetric stretching vibration of aliphatic C-H bonds CH2 groups. The stretching vibration of C-H aromatic was absorbed at 3086 cm-1. The 1H NMR spectrum of the L shows a triplet signal at 2.64 ppm, which can be assigned to Hb (4H), a triplet signal at ca. 3.59 ppm attributed to Ha (4H), a singlet signal due to the Hc (4H) resonance at ca. 4.34 ppm, a singlet signal at ca. 4.59 ppm attributed to Hd (4H). In the aromatic region (7.38-8.04 ppm) four signals were found, a multiplet signal at ca. 7.38 ppm attributed to Hh,i (4H), a multiplet signal at ca. 7.54 ppm attributed to Hf (H), a multiplet signal at ca. 7.84 ppm attributed to Hg,j (4H), a doublet signal at ca. 8.04 ppm attributed to He (2H). The 13C NMR spectrum in the region of aliphatic shows four signals at 42.82, 50.83, 60.65, and 67.78 ppm attributed to Cc, Cb, Ca and Cd, respectively. In the region corresponding to the signals of aromatic ring carbons (113.43164.10 ppm), 12 peaks were observed (Figs. S. 2 - 7).

3.2. Theoretical study The structures of [PbL]2+ was optimized by Density Functional Theory (DFT) calculations using B3LYP/6-31G* basis set. The resulting structure for [PbL]2+ was used for further calculations 4

using the effective core potential (ECP) standard basis set LanL2DZ [17-19] for Pb2+ ion and the standard 6-31G* basis set for all other atoms. The resulting structural diagrams are shown in

Fig. 1 and selected calculated bond distances and angles relating to them are shown in Table 1. Lead is bound by the two amine nitrogens, two etheric oxygens and two oxygen atoms from two ethanolate groups in a distorted octahedral arrangement. The spatial distributions and orbital energies of HOMO and LUMO of [PbL]2+ were also determined (S. 8). It was clearly shown that the HOMO distribution of the complex was located essentially over the naphthalen moieties. The energy gap between HOMO and LUMO was computed to be 4.489 eV (S. 8) corresponding to absorption band of aromatic groups in the Uv-Vis spectrum.

3.3. Spectral properties of fluorescent L Excitation of L at 280 nm gave an emission spectrum composed by a band centered at 359 nm, assigned to the naphthalene groups. To obtain the optimum condition for the photophysical properties of the chemosensor prepared, the pH responses were examined in the aqueous acetonitrile solution (Fig. 2). In the basic condition (pH 8–12), no fluorescent emission was observed (OFF state) due to the photoinduced electron transfer (PET) quenching by the lone pair of electrons on the secondary N donor atoms. However, in the pH range of 1.0–6.0, the typical naphthalene emission was observed. Based on above results, we employed the pH 7.4 condition buffered by HEPES for the measurements of the photophysical properties throughout this study. Under this physiological condition, as expected, L exhibit weak fluorescence emission.

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The sensing properties of compound L toward various metal ions were examined by treating sensor L (5μM) with metal ions such as Na+, K+, Cs+, Mg2+, Ba2+, Sn2+, Pb2+, Cr3+, Mn2+, Fe3+, Fe2+, Co2+, Ni2+, Cu2+, Zn2+, Cd2+, Hg2+ and Ag+ in acetonitrile/H2O (9:1, v/v) mixture at ambient temperature. Significantly, when increasing concentrations of Pb2+ ions were introduced, the emission of L was drastically increased (up to 17-fold enhancement when compared to the fluorescence intensity of free sensor L at 359 nm, see Fig. 3). The weak fluorescence of L was completely quenched by addition Cs+, Sn2+, Cu2+, Fe2+ and Fe3+ ions. The observation that the fluorescence intensity is completely quenched by Cu2+, Fe2+ and Fe3+ is consistent with the fact that these transition metal ions have intrinsic quenching nature [20–22]. The addition of the other metal ions elicited no noticeable changes to the fluorescence spectra of sensor L (Fig. 3). To further investigate the chemosensor properties of L as a sensor for Pb2+, fluorimetric titration of L was performed with the Pb2+ ion in the presence of different concentrations of Pb2+ ions. Figure 4 shows the gradual enhancements in fluorescence intensity for L upon the addition of increasing concentrations of Pb2+ ions. It is shown here that the free ligand L exhibits weak emission. This weak emission is due to photoinduced electron transfer (PET) from the lone pairs of amine nitrogen to the photoexcited naphthalene which leads to fluorescence quenching. Upon addition of Pb2+ ions to solution of receptor L, significant fluorescence enhancement was observed (Fig. 3). This is due to the fact that when Pb2+ ions are added to the receptor L, the lone pair of electrons on nitrogen gets involved in the coordination with the Pb2+ ion. This leads to the decrease in the electron density on nitrogen atom as a result of which the electron transfer from the nitrogen

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to the photoexcited naphthalene moiety is suppressed and hence allows the fluorescence emission. The FEF (fluorescence enhancement factor) values of fluorescent L responding to different metal ions are shown in Fig. 5. The FEF (IX − IL)/IL was calculated using minimal (IL) and maximal (Ix) fluorescence intensities recorded before and after addition of metal ions, respectively. The highest fluorescence enhancement of for L has been observed in the presence of Pb2+ ions. We subsequently studied the chemical reversibility behavior of the binding of L and Pb2+ in the acetonitrile/H2O mixture. Because of the high stability constant of the EDTA-Pb2+ complex, it was anticipated that addition of EDTA will sequester Pb2+ of the metal complex, liberating the free L. With this intention, excess of EDTA was added to the Pb2+ complex of L. The fluorescence of the solution disappeared instantly upon the addition of EDTA, whereas readdition of excess Pb2+ could recover the fluorescence signal (Fig. 6), demonstrating that the binding of L with Pb2+ is chemically reversible. In order to determine the stoichiometry of the H2L- Pb2+ complex, the Job’s method was used [23,24]. In the Job’s plot, a maximum fluorescence change was observed with a 0.5 M fraction of ionophore to Pb2+ for L, which indicated that only a 1:1 complex was formed (Fig. 7). The absorption spectrum of L exhibits structured absorption spectrum corresponding to the ππ* transitions of naphthalene unit observed in naphthalene derivatives. However, the change in the environment of the naphthalene unit in the present systems L causes change in the intensities and positions of the π-π* bands compared to that of pure naphthalene (Fig. 8). 7



3.4. Limit of detection The limit of detection was estimated utilizing the method of gradually decreasing concentration of Pb2+. When the concentration of Pb2+ decreases to 5.0 × 10−7 M, an observable stripping peak was observed. When further decreasing the concentration, the stripping peak almost disappears. So, the limit of detection is evaluated to be 5.0 × 10−7 M.

4. Conclusion Synthesis of L can be achieved very easily in 75% yield by Schiff base condensation of 2-[2(2-formylnaphthoxy)ethoxy]naphthaldehyde [12] with 2-aminoethanol in methanol, followed by reduction with NaBH4. Optimized geometric structures of [PbL]2+ were calculated. L possesses a high affinity and selectivity for lead ions relative to most other competitive metal ions like Na+, K+, Cs+, Mg2+, Ba2+, Cr3+, Mn2+, Fe3+, Fe2+, Co2+, Ni2+, Cu2+, Zn2+, Cd2+, Hg2+ and Ag+ by enhancement of the fluorescence emission. We expect that the present design strategy and the remarkable photophysical properties of this chemosensor will help to extend applications of fluorescent chemosensor for metal ions.

References [1] D.A. Gidlow, Lead toxicity, Occup. Med. 54 (2004) 76–81. [2] H.W.Mielke, P.L. Reagan, Soil is an important pathway of human lead exposure, Environ. Health Persp. 106 (Suppl. 1) (1998) 217–229. [3] R.A. Goyer, Results of lead research: prenatal exposure and neurological consequences, Environ. Health Persp. 104 (1996) 1050–1054. [4] S. Sanchez, A.R. Perez, S. Genta, M. Aybar, E. Villecco, R.A. Sanchez, Renal

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extracellular matrix alterations in lead-treated rats, J. Appl. Toxicol. 21 (2001) 417–423. [5] D.A. Daggett, E.F. Nuwaysir, S.A. Nelson, L.S. Wright, S.E. Kornguth, F.L. Sietel, Effects of triethyl lead administration on the expression of glutathione S-transferase isoenzymes and quinone reductase in rat kidney and liver, Toxicology 117 (1997) 61–71. [6] M.J.J. Ronis, T.M. Badger, S.J. Shema, P.K. Roberson, F. Sheikh, Reproductive toxicity and growth effects in rats exposed to lead at different periods during development, Toxicol. Appl. Pharmacol. 136 (1996) 361–371. [7] A. Skoczyn´ ska, J.Wrobel, R. Andrzejak, Lead–cadmiuminteraction effect on the responsiveness of rat mesenteric vessels to norepinephrine and angiotensin II, Toxicology 162 (2001) 157–170. [8] H.G. Preuss, G. Jiang, J.W. Jones, P.O. Macarthy, P.M. Andrews, J.A. Gondal, Early lead challenge and subsequent hypertension in Sprague–Dawley rats, J. Am. Coll. Nutr. 13 (1994) 578–583. [9] M. de la Guadia, A.R. Maur, C. Mongay, Atomic absorption spectrometric determination of gasoline additives by vapour phase sample introduction, J. Anal. At. Spectrom. 3 (1988) 1035–1038. [10] J.R. Garbarino, H.E. Taylor, Stable isotope dilution analysis of hydrologic samples by inductively coupled plasma mass spectrometry, Anal. Chem. 59 (1987) 1568–1575. [11] W.W. Van Berker, F.J.M.Maessen, Use and evaluation of poly(dithiocarbamate) in electrothermal vaporization inductively coupled plasma atomic emission spectrometry for simultaneous trace analysis of seawater and related biological materials, Spectrochim. Acta Part B 34 (1988) 1337–1347. [12] R. Azadbakht, M. Parviz, E, Tamari, H. Keypour, R. Golbedaghi, Spectrochim. Acta, A 82 (2011) 200– 204.

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[13] A.D. Becke, J. Chem. Phys. 98 (1993) 5648-5652. [14] C. Lee, W. Yang, R.G. Parr, Phys. Rev. B. 37 (1988) 785-789. [15] M. J. Frisch, G. W. Trucks, H. B. Schlegel, G. E. Scuseria, M. A. Robb, J. R. Cheeseman, J.A. Montgomery, Jr., T. Vreven, K. N. Kudin, J. C. Burant, J. M. Millam, S. S. Iyengar, J. Tomasi, V. Barone, B. Mennucci, M. Cossi, G. Scalmani, N. Rega, G. A. Petersson, H. Nakatsuji, M. Hada, M. Ehara, K. Toyota, R. Fukuda, J. Hasegawa, M. Ishida, T. Nakajima, Y. Honda, O. Kitao, H. Nakai, M. Klene, X. Li, J. E. Knox, H. P. Hratchian, J. B. Cross, V. Bakken, C. Adamo, J. Jaramillo, R. Gomperts, R. E. Stratmann, O. Yazyev, A. J. Austin, R. Cammi, C. Pomelli, J. W. Ochterski, P. Y. Ayala, K. Morokuma, G. A. Voth, P. Salvador, J. J. Dannenberg, V. G. Zakrzewski, S. Dapprich, A. D. Daniels, M. C. Strain, O. Farkas, D. K. Malick, A. D. Rabuck, K. Raghavachari, J. B. Foresman, J. V. Ortiz, Q. Cui, A. G. Baboul, S. Clifford, J. Cioslowski, B. B. Stefanov, G. Liu, A. Liashenko, P. Piskorz, I. Komaromi, R. L. Martin, D. J. Fox, T. Keith, M. A. Al-Laham, C. Y. Peng, A. Nanayakkara, M. Challacombe, P. M. W. Gill, B. Johnson, W. Chen, M. W. Wong, C. Gonzalez, and J. A. Pople, Gaussian, Inc., Pittsburgh PA, (2003). [16] Hyperchem, Release 5.02; Hypercube: Gainesville, FL, (1997). [17] K.D. Dobbs, W.J. Hehre, J. Comp. Chem. 8 (1987) 880–893. [18] P.J. Hay, W.R. Wadt, J. Chem. Phys. 82 (1985) 299–310. [19] P.C. Hariharan, J.A. Pople, Theor. Chim. Acta 28 (1973) 213–222. [20] K. Rurack, Spectrochim. Acta A 57 (2001) 2161–2195. [21] Y. Ma, W. Luo, P.J. Quinn, Z. Liu, R.C. Hider, J. Med. Chem. 47 (2004) 6349–6362. [22] B. Bodenant, T. Weil, M. Businelli-Pourcel, F. Fages, B. Barbe, I. Pianet, M. Laguerre, J. Org. Chem. 64 (1999) 7034–7039. [23] W.C. Vosburgh, G.R. Cooper, J. Am. Chem. Soc. 63 (1941) 437–442.

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[24] R.R. Avirah, K. Jyothish, D. Ramaiah, Org. Lett. 9 (2007) 121–124.

Fig. 1. B3LYP optimized structure of [PbL]2+ .

Table 1. The selected bond lengths (Å) and angles (˚) for [PbL]2+. Bond length (Å)

Bond angle (˚)

Pb(1)-N(1)

2.608

N(1)-Pb(1)-N(2)

164.35

Pb(1)-N(2) Pb(1)-O(1)

2.606

O(3)-Pb(1)-O(4)

163.85

2.435

N(1)- Pb(1)-O(3)

66.07

Pb(1)-O(2) Pb(1)-O(3) Pb(1)-O(4)

2.435 2.599 2.600

O(3)- Pb(1)-O(2)

77.20

O(2)- Pb(1)-N(2) O(1)- Pb(1)-O(2) O(4)- Pb(1)-N(2) O(4)- Pb(1)-O(1) O(2)- Pb(1)-N(1) O(1)- Pb(1)-N(1) O(1)- Pb(1)-N(2)

66.39 65.75 63.03 77.18 91.63 66.41 91.59

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1000

PH=1 PH=2 PH=3 PH=4 PH=5 PH=6 PH=7 PH=8 PH=9 PH=10 PH=11 PH=12 PH=13 PH=14

900 800 Fl. Intensity

700 600 500 400 300 200 100 0 320

340

360

380

400

420

440

Wavelength (nm)

Fig. 2. Fluorescence response of L in the absence of metal ions at different pH values.

1000

Pb2+

Fl. Intensity

800 Mn2+ , Zn2+ Cd2+ , Mg2+ , Ba2+ Ni2+ , Co2+ , Ag+ Na+ , K+ , Ca2+ Hg2+ ,L Cs+ , Sn2+ Cu2+ , Fe 3+ , Fe 2+

600 400 200 0 320

340

360

380

400

420

440

Wavelength (nm)

Fig. 3. Fluorescence spectrum of L (5µ M) in the presence of various metal ions Na+, K+, Cs+, Mg2+, Ba2+, Sn2+, Pb2+, Cr3+, Mn2+, Fe3+, Fe2+, Co2+, Ni2+, Cu2+, Zn2+, Cd2+, Hg2+ and Ag+ (1000µ M). Both the excitation and emission slit widths were 5.0 nm.

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1000

[Pb2+]/[L] 1.2 1000 1.1 1.0 800 0.9 600 0.8 0.7 400 0.6 200 0.5 0.4 0 0.3 0.2 0.1 0.0

900 800

I/I 0

Fl. Intensity

700 600 500 400 300 200

0

0.5

1

[Pb2+ ]/[L]

100 0 320

340

360

380

400

420

440

Wavelength (nm)

Fig. 4. Changes in the fluorescence spectra of L (5µM) as a function of added Pb2+ concentration in acetonitrile/H2O. Excitation wavelength was 288 nm. Both the excitation and emission slit widths were 5.0 nm. 15 13

(IX-IL)/IL

11 9 7 5 3 1 -1

Fig.5. The fluorescence enhancement factor (FEF) of L upon addition of various metal ions in methanol at 25 ºC. Both the excitation and emission slit widths were 5.0 nm.

13

1000

1 L

Fl. Intensity

800

L+Pb(ll)=1

3

1+EDTA=2

600

2+Pb(ll)=3

400

2 200

L 0 320

340

360

380

400

420

440

Wavelength (nm)

Fig. 6. The chemical reversibility behavior of the binding of L and Pb2+ ions

1000

Fluorescence Intensity

900 800 700 600 500 400 300 200 100 0 0

0.1

0.2

0.3

0.4

0.5

0.6

[Pb2+ ]/[Pb2+ ]+[L]

Fig. 7. Job’s plot for addition for L + Pb2+.

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0.7

0.8

0.9

1

0.8

[Pb2+]/[L] 1.2 1.1 1.0 0.9 0.8 0.7 0.6 0.5 0.4 0.3 0.2 0.1 0.0

0.7

Absorbance

0.6 0.5 0.4 0.3 0.2 0.1 0 250

270

290

310

330

350

Wavelength (nm) Fig. 8. Changes in the absorption spectra of L (50µM) as a function of added Pb2+ concentration in acetonitrile/H2O.

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Graphical abstract

Weak fluorescence

hv

Strong fluorescence

hv

O O

NH

HN

Pb2+

Pb2+

NH OH

OH

O

O NH

HO

HO

PET

Highlights ►A new fluorescent chemosensor was prepared. ►The chemosensor exhibits a significant fluorescent enhancement toward Pb2+ in acetonitrile/H2O /H2O. ► In the presence of Pb2+, L exhibits significant fluorescence enhancements owing to PET.

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