Introduction

Iron is one of the essential trace elements in the human body, which plays an important role in many biological activities, including oxygen metabolism (Sundramoorthy et al. 2016; Kim et al. 2013), enzymatic catalysis (Nandhini et al. 2016), DNA synthesis (Wei et al. 2015). Both iron deficiency and overload can cause serious problems (Saleem and Lee. 2015; Zhu et al. 2015; Kim et al. 2016). Hypoferremia usually induces anemia and functional deficits, making people become susceptible to disease. Hyperferremia can cause cell/tissue damage and organ dysfunction. It has been reported that Alzheimer’s disease is related to iron overload (Sahoo et al. 2012). Thus, developing efficient method to detect iron is imperative.

Up to now, the detection methods of iron ions include flow injection analysis (Elsuccary and Salem 2015), atomic absorption spectroscopy (Shamspur et al. 2005), cyclic voltammetry (Caprara et al. 2015), and chemosensors (Au-Yeung et al. 2013) et al. Compared with the instrumental analysis methods, time-consuming and high cost, chemosensors, especially fluorescent and the “naked eyes” colorimetric recognition methods are convenient, fast and cheap. However, numbers of fluorescent probes are non-emissive in aqueous solution for the aggregation-caused quenching (ACQ) effect which limited their practical applications. Aggregation-induced emission enhancement (AIEE) fluorophores are weak emission in dilute solutions and strongly emit in aggregation states, which open a way to design chemosensors to against ACQ (Mei et al. 2014, 2015). The α-cyanostilbene derivatives are representative AIEEgens (An et al. 2002). Based on our previous work, α-cyanostilbene unit functionalized with chelating group is an effective method for designing ions probes (Fang et al. 2016). Terpyridine group has strong metal chelating ability and has unique advantages in the design of iron ions recognition probes (Ali et al. 2011; Brombosz et al. 2007). However, in the previous reports, most fluorophores detecting Fe2+ suffer from the interference of other metal ions, especially Fe3+. Recently, a graphene oxide-terpyridine conjugate as a nano-chemosensor for Fe2+ in aqueous media was reported (Eftekhari-Sis and Mirdoraghi 2016), nevertheless, specific terpyridine functionalized Fe2+ probe was rare according to our investigation. Our group managed developing two kinds of terpyridine functionalized α-cyanostilbene derivatives which detected Fe2+ in aqueous environment (Liang et al. 2007; Zhang et al. 2014). Herein, we imagined to introduce carbazole unit, a famous fluorophores with high luminescence efficiency, hole-transporting moiety into the system to design a selective Fe2+ probe with AIEE properties.

In this work, a novel carbazole derivative with functionalized terpyridine (L) was synthesized. The photophysical properties of L were studied by UV–vis absorption spectroscopy and fluorescence spectroscopy. This sensitive probe exhibited excellent AIEE property and could be used to detect single Fe2+ in aqueous solution. Other metal ions including Fe3+ caused little interference. Fortunately, L could act as a dual mode Fe2+ sensor via UV–vis absorption spectroscopy and “naked eyes” recognition.

Experimental

All chemicals were commercially available and all solvents were purified by conventional methods before used. NMR spectra were recorded on a Bruker Avance 400 MHz spectrometer using CDCl3 or DMF-d 7 as solvent. Chemical shifts were reported in parts per million (ppm) down field from TMS with the solvent resonance as the internal standard. Coupling constants (J) were reported in Hz and referred to apparent peak multiplications. Mass spectra were recorded on an Agilent 6410 LC–MS/MS system (USA) equipped with an electrospray ion source (ESI). UV–vis absorption spectra were recorded on a TU-1901 of Beijing Purkinje General Instrument Co., Ltd, spectrometer (slit: 5 nm, 3 nm) using samples in solutions. Fluorescence spectra were recorded with a RF-5301 PC fluorescence spectrometer. The stock solution (1 × 10−3 M) was prepared by dissolving probe L in DMF. For the UV–vis and fluorescence analysis, 50 μL of the stock solution of L in DMF was diluted to 5 mL DMF-H2O mixture or EtOH-H2O mixture (volume fraction of water accounts for 30%), respectively. Solutions of MgSO4, Al2(SO4)3·18H2O, MnSO4·H2O, FeSO4·7H2O, FeCl3·6H2O, CoCl2·6H2O, NiCl2·6H2O, CuSO4·5H2O, ZnSO4·7H2O, AgNO3, CdSO4·8H2O, BaCl2·2H2O, Hg(ClO4)2·3H2O, and Pb(NO3)2 were prepared by dissolving them in double distilled water. All samples were prepared at room temperature. The emission spectra were recorded when excited at 430 nm. All the measurements were carried out at room temperature.

The synthetic route of compound L was shown in Fig. 1. Compound 1 was prepared according to the literature methods (Jin et al. 2011; Constable and Ward. 1990; Potts and Konwar. 1991).

Fig. 1
figure 1

The synthetic route of compound L

9-(4-Bromobutyl)-9H-carbazole (2): a mixture of carbazole (3.3 g, 20 mmol), 1,4-dibromobutane (20 mL), toluene (15 mL), and tetrabutylammonium bromide 1.0 g in 15 mL 50% aqueous sodium hydroxide solution were stirred at 45 °C for 3 h, and then cooled to RT. The mixture was stirred overnight. After extraction with CH2Cl2, the organic phase was washed by water and saturated salt water for three times, respectively, and dried with anhydrous sodium sulfate. The solvent was removed under reduced pressure. The crude product was recrystallized from ethanol to obtain a white powder (3.83 g, 66.3% yield).

9-(3-Bromopropyl)-9H-carbazole-3-carbaldehyde (3): 5.4 mL DMF (70 mmol), 6.4 mL (70 mmol) POCl3 were cooled to 0 °C by an external ice bath. Later, compound 2 (7.0 g, 23.2 mmol) dissolved in 1,2-dichloroethane was added to the mixture. The mixture was stirred at 80 °C overnight, then, it was added to ice water. After neutralization to weak basicity by NaOH, the solution was extracted with CH2Cl2. The organic layer was dried over with anhydrous sodium sulfate and filtered. The solvent was removed under reduced pressure. The residue was purified by silica gel column chromatography (eluent: CH2Cl2) to afford a white solid (4.29 g, 56.1% yield). m. p. 83–85 °C; 1H NMR (CDCl3, 400 MHz) δ 1.828–1.898 (2H, m, CH2), 2.067–2.140 (2H, m, CH2), 3.532–3.563 (2H, t, J = 6.0 Hz, CH2–O), 4.391–4.427 (2H, t, J = 7.2 Hz, CH2–N), 7.331–7.367 (1H, t, J = 7.2 Hz, phenyl–H), 7.459–7.498 (2H, t, J = 8.0 Hz, phenyl–H), 7.537–7.575 (1H, t, J = 7.6 Hz, phenyl–H), 8.019–8.040 (1H, d, J = 8.4 Hz, phenyl–H), 8.164–8.184 (1H, d, J = 8.0 Hz, phenyl–H), 8.627 (1H, s, phenyl–H), 10.112 (1H, s, aldehyde–H); 13C NMR (CDCl3, 100 MHz): 26.356, 29.987, 42.676, 44.341, 108.826, 109.263, 120.506, 120.842, 123.066, 123.187, 123.949, 126.862, 127.312, 128.727, 141.044, 143.931, 191.688.

N-(2,2′:6,2″,-4- terpyridyl oxybutyl)-3-aldehyde carbazole (4): Compound 1 (145.0 mg, 484.5 μmol), compound 3 (160.0 mg, 484.5 μmol), and K2CO3 (80.4 mg, 581.7 μmol) were added in 4 mL acetonitrile and refluxed overnight. The hot mixture was filtrated. The residue was washed with acetonitrile and water. After using flash chromatography (eluent: CH2Cl2) to remove compound 3, the crude product was purified with chromatography (CH2Cl2/methanol = 10/1) to give a white solid product (118.0 mg, 48.9% yield). m.p. 180–181 °C; 1H NMR (CDCl3, 400 MHz), δ 1.909–1.976 (2H, t, J = 13.7, 7.3 Hz, CH2), 2.129–2.202 (2H, m, CH2), 4.240–4.269 (2H, t, J = 5.9 Hz, CH2–N), 4.456–4.491 (2H, t, J = 7.1 Hz, CH2–O), 7.304–7.355 (3H, m, phenyl–H), 7.485–7.564 (3H, m, phenyl–H), 7.839–7.881 (2H, m, phenyl–H), 7.987–8.030 (3H, m, phenyl–H), 8.141–8.160 (1H, d, J = 7.6 Hz, phenyl–H), 8.609–8.686 (5H, m, phenyl–H), 10.086 (1H, s, aldehyde–H); 13C NMR (CDCl3, 100 MHz,): 25.761, 26.700, 43.096, 67.581, 107.351, 108.944, 109.369, 120.427, 120.802, 121.411, 123.066, 123.192, 123.910, 126.863, 127.425, 128.653, 136.923, 141.118, 144.018, 148.954, 155.927, 157.061, 166.980, 191.748.

N-(2,2′:6,2″,-4-terpyridyl oxybutyl)-3-[2-(4-nitrophenyl)-2-cyano]vinyl carbazole (L): Compound 4 (100.0 mg, 200 μmol), 2-(4-nitrophenyl)acetonitrile (39.0 mg, 240.5 μmol), 2 mL tetrahydrofuran and a drop of piperidine were added into 4 mL ethanol. The mixture was refluxed for 8 h and filtered. The residue was recrystallized from ethanol as an orange powder (50.0 mg, 38.8% yield). m.p. 261–263 °C; 1H NMR (DMF-d 7, 400 MHz), δ 2.225 (2H, s, CH2), 2.395 (2H, s, CH2), 4.562–4.591 (2H, t, J = 5.8 Hz, CH2–N), 4.906–4.941 (2H, t, J = 6.9 Hz, CH2–O), 7.517–7.554 (1H, t, J = 7.4 Hz, phenyl–H), 7.681–7.712 (2H, m, phenyl–H), 7.762–7.803 (1H, d, J = 8.0 Hz, phenyl–H), 8.051–8.071 (2H, d, J = 7.9 Hz, phenyl–H), 8.176 (2H, s, phenyl–H), 8.337–8.359 (1H, d, J = 8.7 Hz, phenyl–H), 8.405–8.424 (2H, t, J = 8.3 Hz, phenyl–H), 8.542–8.584 (2H, m, phenyl–H), 8.617–8.640 (2H, d, J = 9.1 Hz, phenyl–H), 8.707 (1H, s, phenyl–H), 8.877–8.929 (4H, m, phenyl–H), 9.134 (1H, s, CH); HR-MS (ESI–MS): m/z = 643.2466, calcd for [C40H31N6O3]+ = 644.2458 ([M+H]+).

Results and discussion

Water is a poor solvent and DMF is a good solvent for compound L. In DMF-H2O mixed solvent, with the increase of water fraction (f w), UV–vis absorption spectra showed broadened absorption accompanying with a red-shift (Fig. 2a). The light scattering tails were the characteristic of Mie effect, suggesting that compounds formed J-aggregate (Liang et al. 2016). In Fig. 2b, the peak at 425 nm in the transmittance spectra became weak when f w changed from 10 to 30 vol%. Later the transmittance started to decrease while water continually added. The peak reappeared when f w was above 80 vol%, which was consistent with the absorption peak in UV–vis absorption spectra. In Fig. 2c, compound L had faint emission in pure DMF solution. With an increasing content of water from 0 to 60 vol%, the emission decreased swiftly. The decreased solubility of compound L in the aqueous mixture with high water content induced aggregate formation, which boosted the fluorescence emission. After f w was above 90 vol%, the emission intensity of compound L began to decrease slightly. It is remarkable that the formation of J-aggregate expanded the area of π-conjugation, which was also in favor of the enhancement of emission. All of the above indicated that compound L exhibited obvious AIEE property.

Fig. 2
figure 2

UV–vis (a) and transmittance (b) and emission (c) spectra of compound L (10 μM) in DMF–H2O mixture with volume fractions. Insets relation between fluorescence maximum intensity of compound L and volume fraction of water

To evaluate the recognition ability of compound L to metal ions, the UV–vis absorption spectra and emission spectra of L in the same concentration of metal ions were determined. As shown in Fig. 3, the solution with Fe2+ turned to brick red, while some other solutions such as solution with Mg2+ or Pb2+ exhibited a negligible light green color. The main reason was a characteristic peak formed in UV–vis absorption spectra at 557 nm when Fe2+ was added (Fig. 4a). This phenomenon was attributed to metal-to-ligand-charge-transfer (MLCT) (Meier and Schubert. 2005). To identify Fe2+ state after FeSO4·7H2O was added into L in EtOH, the mixture was evaporated in vacuum. The XPS experiment results verified there were Fe2+ existed in the mixture (Fig. S6). It was indicated that compound L had specific colorimetric recognition towards Fe2+, which could be used as a method of fast “naked eyes” detection. Moreover, after adding Fe2+, the emission quenched much more sharply than that of other metal ions (Fig. 4b). Therefore, compound L could also become a fluorescent probe for Fe2+. More evidence is shown in Fig. 5. After adding Fe2+, the absorbance at 557 nm of L was three times more than other metal ions, indicating that other metal cations caused little interference in absorbance.

Fig. 3
figure 3

Color change of compound L (10 μM) in the presence of metal ions in EtOH–H2O mixed solvent

Fig. 4
figure 4

UV–vis (a) and emission (b) spectra of compound L (10 μM) in EtOH–H2O mixture (volume fraction of water accounts for 30%) after adding equivalent of various metal ions

Fig. 5
figure 5

Absorbance at 557 nm of compound L (10 μM) in EtOH–H2O mixed solvent after adding equivalent of various metal ion. X-axis: A blank, B Mg2+, C Al3+, D Mn2+, E Fe2+, F Fe3+, G Co2+, H Ni2+, I Cu2+, J Zn2+, K Ag+, L Cd2+, M Ba2+, N Hg2+, and O Pb2+

To investigate the interaction between compound L and Fe2+, a titration experiment was studied. The concentration of L was 1.0 × 10−5 M. As shown in Fig. 6a, with the increase of Fe2+ concentration, a new peak at 557 nm in UV–vis absorption spectra was observed. The absorbance began increasing linearly with the titration of Fe2+ then it reached a maximum as soon as Fe2+ was 5 μM. A binding 2:1 stoichiometry (L: Fe2+) was further verified by Job’s plot (Fig. 7). In order to test the sensitivity of Fe2+, we studied fluorescent titration as shown in Fig. 6b. When the concentration of Fe2+ varied from 0 to 5 μM, the emission was weaken obviously, accompany with the peak at 560 nm blue-shifted by 30 nm. Then it changed very slowly. The limit of detection was calculated as low as 1.63 μM. The formula used was: DL = 3δ/S, where δ is the standard deviation of blank measurement, S is the slope between the ratio of absorbance versus respective analyte concentration.

Fig. 6
figure 6

UV–vis (a) and emission (b) spectra of compound L (10 μM) in EtOH–H2O mixture (volume fraction of water accounts for 30%). Insets relation between absorbance of compound L at 557 nm and concentrations of Fe2+

Fig. 7
figure 7

Job’s plot curve of L with Fe2+ ions

The binding behavior of L towards Fe2+ ions and other competitive metal cations was investigated. The black bars represented the absorbance of one equivalent of L mixed with one equivalent of other metal ions and Fe2+ ions. As shown in Fig. 8, except for Co2+ and Cu2+, no significant interference was observed, indicating that L could detect Fe2+ in presence of other metal ions.

Fig. 8
figure 8

Bars represent competitive selectivity of L (10 μM) in solvent mixture of EtOH–H2O (volume fraction of water accounts for 30%) toward Fe2+ cation. X-axis: A Fe2+, B Mg2++Fe2+, C Al3++Fe2+, D Mn2++Fe2+, E Fe3++Fe2+, F Co2++Fe2+, G Ni2++Fe2+, H Cu2++Fe2+, I Zn2++Fe2+, J Ag++Fe2+, K Cd2++Fe2+, L Ba2++Fe2+, M Hg2++Fe2+, and N Pb2++Fe2+

Conclusions

In conclusion, we designed and synthesized a novel terpyridine modified carbazole derivative L, which had excellent AIEE property in aqueous environment. This probe could specifically detect Fe2+ by “naked eyes” colorimetric recognition and fluorescent recognition in the mixed solvent of EtOH–H2O (f w = 30%), with high sensitivity. The limit of detection was determined to be 1.63 μM. We believed that functionalized terpyridine with α-cyanostilbene could be extended as a guide for the further design of AIEE probes detecting transition metal ions.