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A nanofibrous membrane fluorescent sensor for fluoride ions prepared by electrospinning and host-guest interaction

ABSTRACT

A novel inclusion complexes nanofibrous membrane fluorescent sensor was prepared for recognizing F- via electrospinning and host–guest interaction. The host α-cyclodextrin on the surface of the electrospun nanofiber membrane is assembled into the guest azobenzene molecule which modified with F- fluorescent probe, and the formation of the inclusion complex is fixed on the surface of the nanofibrous membrane without external force, to prepare a novel surface controllable composite nanofiber membrane for F- detection. The inclusion complexes nanofibrous membrane exhibited favourable sensitivity and selectivity for F-. The introduction of F- would result in notable fluorescent decreasing of the membrane, but the other most common anions would not disturb the detection of F-. Moreover, this nanofibrous membrane was not only a fluorescent sensor for detecting F-, but also a good adsorbent for F- in solution.

Keywords
Host–guest interaction; Nanofibrous membrane; Fluorescent sensor; Fluoride ions; Adsorbent

1. INTRODUCTION

F- is a very common anion in the environment, it always exists in the form of various compounds. Moreover, F- is also widely used in industrial production,such as manufacture of plastics and rubber, the production of rodenticide pharmaceutical and pesticide [11 YANG, L., DONG, T., REVANKAR, H. M., et al., “Recent progress on fluorination in aqueous media”, Green Chemistry, v. 19, n. 17, pp. 3951-3992, Jul. 2017.]. The F- content in human body is about 2.6 g, and 95% of them are distributed in bones and teeth to enhance their structure stability, in the second distributed in hair and nails,and microscale in organs [22 WANG, L.T., XIE, Y.H., YANG, J.L., et al., “Insight into mechanisms of fluoride removal from contaminated groundwater using lanthanum-modified bone waste”, RSC Advances, v. 85, n.7, pp. 54291-54305, Nov. 2017.]. The adsorption of F- in the human body is mainly in water,food and skin, the soluble F- in drinking water is almost absorbed by the small intestine and stomach, and the absorption rate of F- in food is about 50%, moreover, F- can be absorbed in human body by skin and transported to bone through blood [33 RAN, X., GAO, Q.Q., ZHANG, Y., et al., “Colorimetry and phase transition characteristics in sensing fluoride anion based on hydrazide organogelators”, RSC Advances, v. 88, n.7, pp. 56016-56022, Dec. 2017., 44 ALLED, M., FERNANDEZ, A., EDLER, K.J., et al., “Azulene–boronate esters: colorimetric indicators for fluoride in drinking water”, Chemical Communications, v. 53, n.93, pp. 12580-12583, Nov. 2017.]. Excessive F- in the human body will disturb the metabolism of calcium and phosphorus, then damage to skeleton, cardiovascular and nervous system, and even result in pharyngitis, laryngitis, tracheitis, autonomic nerve dysfunction and acid erosion [55 TURAN, I.S., SEVEN, O., AYAN, S., et al., “Amplified chemiluminescence signal for sensing fluoride ions”, ACS Omega, v. 7, n. 2, pp. 3291-3295, Jul. 2017.]. It is vital important to develop chemosensors for F- in the current environment.

With the rapid expansion of fluorescence detection technique, more and more fluorescent sensors were applied to the composite material field,and nanofiber materials have attracted extensive attention due to their good properties [66 WINCK, A.L., SANTOS, J.C.V., LENZ, D.M., et al., “Development and characterization of gas sensors using thin films of polyaniline as active layer”, Revista Materia, v. 23, n. 4, pp. 12259-12268, Sep. 2018., 77 YANG, T., HOU, P., ZHENG, L.L., et al., “Surface-engineered quantum dots/electrospun nanofibers as a networked fluorescence aptasensing platform toward biomarker”, Nanoscale, v. 43, n. 9, pp. 17020-17028, Nov. 2017.]. Electrospinning is a mature technology for fabricating nanofibrous membrane, the membrane prepared in this way is provided with many obvious structural superiority, such as large specific surface area and high porosity, meanwhile the porous reticulation structure is able to promote the diffusion rate of analyte inside nanofibrous membrane effectively, advance the interaction between the analyte and the functional sensors spreaded in the membrane [88 CHANDRAN, G.T., LI, X.W., Ogata, A., et al., “Electrically transduced sensors based on nanomaterials (2012-2016)”, Analytical Chemistry, v. 89, n. 1, pp. 249-275, Jan. 2017.]. This kind of material is very suitable for the construction of fluorescence sensors membrane. The host–guest interactions have been one of the hottest topics in supramolecular chemistry. By choosing the proper host and guest molecules, such as α- cyclodextrin (α-CD) (host) and azobenzene (guest),the self-assembled systems provide the possibility of immobilizing guest derivatives on a variety of substrates, but host–guest interaction was infrequently reported in the preparation of inclusion complexes nanofibrous membrane in previous work [99 RICHARDSON, J., CUI, J.W., BJORNMALM, M., et al., “Innovation in layer-by-layer assembly”, Chemical Reviews, v. 116, n. 23, pp. 14828-14867, Dec. 2016.]. In this research, we fabricate the nanofibrous membrane fluorescent sensor for F- via host–guest interaction and electrospinning. The guest azobenzene modified with F- fluorescent probe is assembled into the host α-cyclodextrin molecule on the surface of the electrospun nanofiber membrane,it is concluded that the formation of the inclusion complex is fixed on the surface of the nanofibrous membrane without external force,to prepare a novel surface controllable composite nanofiber membrane for F- detection, in addition, this study also expands the method for the preparation of composite nanofiber membrane.

2. MATERIALS AND METHODS

All the chemical reagents and solvents used for synthesis were obtained from commercial suppliers and used without furtherpurification. Solvents for spectra detection was HPLC reagent without fluorescent impurity. Solutions of different ions in titration and selectivity experiments were prepared with tetrabutylammonium salt of anions (CN, F, Cl, AcO, NO3, HSO4, I, H2PO4, ClO4-, PO43-, SO42-, HPO42- and HS- ) in HEPES-NaOH buffer solution at pH 7.1,all pH measurements were performed with a PHS-3C meter, the stock solution of probe was prepared in ethanol. The test samples were prepared by adding accurate amounts of ions stock into corresponding concentration solution of probe [CH3CN:H2O =1: 1, pH = 7.1]. For fluorometric analysis, the fluorescence spectra measurements were performed on a Hitachi F-4500 spectrofluorimeter, the excitation wavelength was set as 319 nm, and emission wavelength was collected from 450 to 675 nm; both the excitation and emission slit widths were set as 5 nm and 5 nm, respectively. The FTIR measurements were performed on a BIO-RAD FTS135 Fourier Transform Infrared Spectrometer, KBr as tablet method with a resolution of 4 cm-1, measuring range 400~4000. The SEM measurements were performed on a JEOL JSM-7610F scanning electron microscope analyzer.

2.1 Synthesis of intermediate 1 [1010 LU, C.L., XU, Z.C., CUI, J.N., et al., “Ratiometric and highly selective fluorescent sensor for cadmium under physiological pH range: a new strategy to discriminate cadmium from zinc”, Journal of Organic Chemistry, v. 72, pp. 3554-3557, Apr. 2007.]

4-Bromo-1,8-naphthalic anhydride (5.51 g, 2.33 mmol) was dissolved in 150 mL ethanol at 70 ℃,and butylamine (1.6 mL, 22.03 mmol) was added dropwise into the solution under stirring. The mixture was refluxed for 2 h and cool down to 25 ℃,then distilled solvent to obtain crude product, the column chromatography was utilized to purify the crude product (EtOH: CH2Cl2 = 1:15) from silica gel, the intermediate 1 was collected as white solid (3.70 g, yield 52 %). Take the above product(1.10g, 5.0 mmol)and ethanediamine (1.51 g, 25 mmol) in 50 mL ethylene glycol monomethyl ether. The mixture was refluxed for 2 h then cool down to room temperature, then remove the solvent,the crude product was purified by recrystallization to obtain intermediate 1 as yellow solid (4.60 g, yield 82 %).

2.2 Synthesis of intermediate 2

P-amido-azobenzene (0.70 g, 3.60 mmol) and triethylamine (1.1 mL,7.9 mmol) were dissolved in 40 mL diethylene oxide,then took thiophosgene (0.3 mL,3.70 mmol) into the solution under N2 protection. Heating up the mixture to 60 ℃ with stirring for 3 h. The solvent was distilled and the crude product was extract with CH2Cl2 and water with 3 times,collect the organic phase and remove CH2Cl2,the crude product was purified by column chromatography (petroleum ether: CH2Cl2 = 1:1) on silica gel to obtain intermediate 2 as orange crystal (1.62 g, yield 90 %).

2.3 Synthesis of intermediate 3

Intermediate 1 (0.75 g,2.5 mmol) and intermediate 2 (0.58 g, 2.5 mmol) were dissolved in 50 mL DMF at 80 ℃ for 8 h,then distilled DMF to obtain crude product, the column chromatography was utilized to purify the crude product (MeOH: CH2Cl2 = 1:15) from silica gel, the intermediate 3 was collected as yellow solid (0.98 g, yield 74 %).

2.4 Synthesisof PAN-co-AA/α-CD

Acroleic acid (3.60 g, 0.05mol) and acrylonitrile (15 g, 0.29 mmol) were dissolved in 75 mL DMF and heated to 50 ℃,then PVP (0.019 g) and AIBN (0.186 g) were added into the solution and keep heating for 4 h. Heat the mixture up to 90 ℃ for 10 h, then 500 mL deionized water was taken into the solution,and collected the generated white precipitates. Washed the precipitates with deionized water for 3 times,and dried them under vacuum at 40 ℃ for 12 h. The PAN-co-AA was obtained as white solid (18.69 g, yield 38 %). PAN-co-AA (5.0 g) was dissolved in 80 mL DMF. EDCI(19.17 g,0.1 mol),DMAP(1.22 g,0.01 mol)and α-CD(102.13 g,0.1 mol)were dissolved in 500 mL DMF and added dropwise into the PAN-co-AA/DMF solution, kept the mixture stirring for 12 h at room temperature, the solvent was distilled and the crude product was taken into deionized water. Collected the generated white precipitates and washed them with deionized water for 3 times, and dried them under vacuum at 40 ℃ for 12 h to obtain PAN-co-AA/α-CD (11.05 g).

2.5 Preparation of PAN-co-AA/α-CD nanofibrousmembrane [1111 WANG, W., WANG, X.L., YANG Q.B., et al., “A reusable nanofibrous film chemosensor for highly selective and sensitive optical signaling of Cu2+ in aqueous media.”, Chemical Communications? v. 49, n. 42, pp. 4833-4835, Apr. 2013.]

PAN-co-AA/α-CD (2.0 g) was dissolved in DMF (8.0 g) for rapidly stirring 24 h at 25 ℃. The resulting 20. wt% precursor solution clear homogenous solution was utilized for electrospinning the nanofibrous membrane. The device for electrospinning process was illustrated as Scheme 2, it was comprised of high - voltage supply, syringe and aluminum foil receiver. In the course of the electrospinning, the high-voltage supply was set as 18 kV, the syringe was at a distance of 15 cm from the aluminum foil, the velocity of spinning was controlled by a microinjector at 4 mL h-1, and the experimental environment is adjusted to 25℃ by air conditioning. After about 2.5 h, the nanofibrous membrane completely covered in the receiver, then picked up the generated membrane by a tweezer from the aluminum foil.

2.6 Preparation of self assembled inclusion complexes of intermediate 3 and PAN-co-AA/α-CD nanofibrousmembrane [1212 WANG, W., WONG, N.K., SUN, M.D., et al., “Regenerable fluorescent nanosensors for monitoring and recovering metal ions based on photoactivatable monolayer self-assembly and host-guest interactions”, ACS Applied Materials and Interfaces, v.7, n. 16, pp. 8868-8875, Apr. 2015.]

Intermediate 3 (0.5 g) was dissolved in 100 mL acetonitrile aqueous solution(CH3CN:H2O = 7:3)with stirring at 50 ℃. Then PAN-co-AA/α-CD nanofibrous membrane (size:1.5cm × 2cm) was taken into the solution with slowly stirring for 30 h. Then cooled down the mixture to room temperature and alternate washed them with deionized water and methanol for 3 times. After vacuum desiccation, the inclusion complexes of intermediate 3 and PAN-co-AA/α-CD nanofibrous membrane was obtained.

Figure 1
Synthesis of intermediate 3
Figure 2
Synthesis of inclusion complexes of intermediate 3 and PAN-co-AA/α-CD nanofibrous membrane

3. RESULTS

3.1 FT-IR investigations of inclusion complexes

FT-IR was utilized to confirm that intermediate 3 was successfully assembled into PAN-co-AA/α-CD nanofibrous membrane. Figure 1(a), 1(b) and 1(c) displayed the FT-IR spectra of PAN-co-AA/α-CD nanofibrous membrane, intermediate 3 and inclusion complexes of intermediate 3 and PAN-co-AA/α-CD nanofibrous membrane, respectively. The bending vibrations at 2923 cm-1 in Figure 1(a) testified the –CH2- in α-CD, the band at 1121 cm-1 represented -OH in α-CD, meanwhile the band at 906 and 1641 cm-1 were ascribed to the stretching vibration of =C-H and C=C in monomer PAN-co-AA. The characteristic bands around 1660 cm-1 in Figure 1(b) represented the N=N, which validated azobenzene was successfully introduced in intermediate 3 [1313 BIAN, Q., WANG, W.S., WANG, S.T., et al. “Light-triggered specific cancer cell release from cyclodextrin/azobenzene and aptamer-modified substrate”, ACS Applied Materials & Interfaces, v. 40, n. 8, pp. 27360-27367, Oct. 2016.]. The band at 1220 represented C=S in the structure, moreover, the band was occurred at 2955 cm-1 proved the existence of N-H in intermediate 3 [1414 LIU, B., TIAN, H., “A selective fluorescent ratiometric chemodosimeter for mercury ion”, Chemical Communications, v. 25, n. 7, pp. 3156-3158, Jul. 2005.]. Furthermore, the above-mentioned characteristic bands in Figure 1(a) and 1(b) all appeared in Figure 1(c) this confirmed that intermediate 3 was successfully assembled into PAN-co-AA/α-CD nanofibrous membrane.

Figure 3
FT-IR spectrum of (a) intermediate 3,(b) PAN-co-AA/α-CD nanofibrous membrane, and (c) inclusion complexes of intermediate 3 and PAN-co-AA/α-CD nanofibrous membrane

3.2 Morphologies of inclusion complexes nanofibrousmembrane

The SEM images of the inclusion complexes nanofibrous membrane under 50 μm and 2 μm were shown in Figure 2. It was informed that the inclusion complexes nanofibrous membrane was composed of massive nanofibers in different directions,and no apparent critical fracture or defect were occurred on the nano-fiber. The average diameter (D) of nanofibers could be calculated from the following equation (1) [1515 ZHOU, C., LIU, H., “A novel nanofibrous film chemosensor for highly selective and sensitive optical signaling of Zn2+”, Journal of the Brazilian Chemical Society, v. 28, n. 10, pp. 1947-1952, Oct. 2017. ].

D   =   1 n Σ i = 1 n X i * B L (1)

where n represents the number of the nanofibers in SEM images, B and L refer to the scale bar and length of the scale bar, respectively. X represents the diameter of independent nanofiber. The average diameter of the nanofiber is calculated to be 0.89 μm based on Figure 2b. Meanwhile, the inclusion complexes nanofibrous membrane take on obvious porous reticulation structure with large specific surface area,this preponderant configuration is able to promote the diffusion rate of F- inside nanofibrous membrane and distinctly accelerate the recognition efficiency [1616 MIN, M.H., WANG, X.F., CHEN, Y.M., et al., “Highly sensitive and selective Cu2+ sensor based on electrospun rhodamine dye doped poly(ether sulfones) nanofibers”, Sensors and Actuators B: Chemical, v. 188, n. 7, pp. 360-366, Nov. 2013.].

Figure 4
SEM image of the inclusion complexes nanofibrous membrane under different scales (a. SEM image under 50 μm, b. SEM image under 2 μm)

4. Discussion

4.1 Response of the inclusion complexes nanofibrousmembrane to F-

The sensitivity of inclusion complexes nanofibrous membrane toward F- was tested by means of titration experiments. The inclusion complexes nanofibrous membrane were cut to fixed size (size:0.8 cm × 1.5 cm) and immersed in CH3CN and buffer solution (HEPES-NaOH, pH 7.1) in titration experiments (CH3CN:H2O =1: 1). The fluorescence response upon of the inclusion complexes nanofibrous membrane depend on various concentration of F- was investigated. As shown in Figure 3, the nanofibrous membrane displayed strong fluorescence at 527 nm (excited at 450 nm),with the increase of F- concentration in the system (0-200μM),the fluorescence intensity at nm decreased obviously. And we can clearly distinguish the fluorescence change of the membrane before and after added F- under the irradiation of a UV-lamp. This significant decrease of 527 nm emission is due to the hydrogen bonding of the acceptor moiety distributed on the surface of the membrane,as F- possess strong electronegativity, its introduction forms hydrogen bonds with H+ in NH, and the deprotonation of N leads the electrons transfer to the Homo orbit in the conjugated plane of the excited state of naphthalimide through the PET effect, and this prevents the excited state electrons from moving back, and result in fluorescence decreasing [1717 JIAO, S., WANG, X.C., SUN, Y.H., et al., “A novel fluorescein-coumarin-based fluorescent probe for fluoride ions and its applications in imaging of living cells and zebrafish in vivo”, Sensors and Actuators B, v. 262, pp. 188-194, Jun. 2018.]. Moreover, as the velocity of proton transfer is far greater than the general electron coordination velocity, this inclusion complexes nanofibrous membrane have a quick response time to F- [1818 CHANDRAN, G.T., LI, X.W., OGATA, A., et al. “Electrically transduced sensors based on nanomaterials (2012-2016)”, Analytical Chemistry, v. 89, n. 1, pp. 249-275, Nov. 2017.].

Figure 5
Fluorescence emission spectrum of the inclusion complexes nanofibrous membrane in different F- concentrations in CH3CN-H2O solution.

4.2 Selectivity and Competition Experiments

To examine the selectivity of the inclusion complexes nanofibrous membrane towards F- over the other anions, selectivity experiments and competition experiments were investigated. Some common anions in environmental such as F-,Cl-, Br-, I-, CN-, HSO4-, H2PO4-, AcO-, NO3-, ClO4-, PO43-, SO42-, HPO42-, HS- were utilized to test their effect of the inclusion complexes nanofibrous membrane. In selectivity experiments,inclusion complexes nanofibrous membrane (size:0.8 cm × 1.5 cm) was infiltrated in a cuvette with CH3CN solution,then 100 μmol L-1 F-, Cl-,Br-, I-, CN-, HSO4-, H2PO4-, AcO-, NO3- , ClO4-, PO43-, SO42-, HPO42-, HS- in HEPES-NaOH buffer solution (pH 7.1)were taken into the cuvette respectively,as illustrated in the black bar of Figure 4, only F- induced an significant fluorescent decrease at 527 nm in the emission spectra, meanwhile the introduction of other anions did not lead any obvious changes at 527 nm. And we can also clearly distinguish the fluorescent response of different anions on the inclusion complexes nanofibrous membrane under the irradiation of a UV-lamp. Furthermore, the competition experiments were utilized to continue exam the obstruct of the inclusion complexes nanofibrous membrane in the detecting F- from the other anions. Under the same condition, 100 μmol L-1 F- was first introduced in the inclusion complexes nanofibrous membrane to induce fluorescence decrease , then 1 mmol L-1 Cl-,Br-, I-, CN-, HSO4-, H2PO4-, AcO-, NO3-, ClO4-, PO43-, SO42-, HPO42-, HS- were introduced into the fluorescence-attenuated mixed system respectively. As illustrated in the red bar of Figure 4, the F- still resulted in the similar fluorescence changes, so it was convinced that these anions did not interference the detecting for F-. For rationalizing the good selectivity of the inclusion complexes nanofibrous membrane in detecting F-, we think the acceptor moieties distributed on the surface of nanofibrous membrane possess stronger binding capacity for F-, the binding mode blocks the excited state electrons from moving back to emit fluorescence, but for the other anions, their entries are not provided with these traits to decrease the fluorescence,therefore this causation brings out the favorable selectivity of the inclusion complexes nanofibrous membrane to F-.

Figure 6
Selectivity experiments of the inclusion complexes nanofibrous membrane (black bar) and competition experiments of the inclusion complexes nanofibrous membrane (red bar)

4.3 The effect of pH on the sensing capability of the inclusion complexes nanofibrousmembrane

PH is an important factor that affects the ability of the sensor to detect determinand, thus the inclusion complexes nanofibrous membrane was immersed in aqueous solution and F- solution of different pH to test its pH stability. As illustrated in Figure 7, the black dots represent the fluorescence intensity of the inclusion complexes nanofibrous membrane in aqueous solution of pH 3 to 12, it could be seen that the fluorescence intensity was stable from pH 6 to 10, excessive acidity and alkalinity both reduced the fluorescence intensity. In addition, the red dots represent the fluorescence intensity of the inclusion complexes nanofibrous membrane in F- solution from pH 3 to 12. As can be seen from the figure, F- all quenched the fluorescence under different pH conditions, hence the experimental data show that the inclusion complexes nanofibrous membrane has certain pH stability from pH 6 to 10, and verified its potential practical application value.

Figure 7
Effect of pH on fluorescence intensity of the inclusion complexes nanofibrous membrane before and after recognition of F-

4.4 Adsorption kinetics of F- ontothe inclusion complexes nanofibrousmembrane

The inclusion complexes nanofibrous membrane provides a porous reticulation structures, which distinctly accelerate F- to approach the fluorescence sensor groups in the inclusion complexes nanofibrous membrane, meanwhile the specific porous structure also enhanced the adsorption performance of the nanofibrous membrane ">Cl-, Br-, I-, CN-, HSO4-, H2PO4-, AcO-, NO3-, ClO4-, PO43-, SO42-, HPO42-, HS- were utilized to test their effect of the inclusion complexes nanofibrous membrane. In selectivity experiments,inclusion complexes nanofibrous membrane (size:0.8 cm × 1.5 cm) was infiltrated in a cuvette with CH3CN solution,then 100 μmol L-1 F-, Cl-,Br-, I-, CN-, HSO4-, H2PO4-, AcO-, NO3- , ClO4-, PO43-, SO42-, HPO42-, HS- in HEPES-NaOH buffer solution (pH 7.1)were taken into the cuvette respectively,as illustrated in the black bar of Figure 4, only F- induced an significant fluorescent decrease at 527 nm in the emission spectra, meanwhile the introduction of other anions did not lead any obvious changes at 527 nm. And we can also clearly distinguish the fluorescent response of different anions on the inclusion complexes nanofibrous membrane under the irradiation of a UV-lamp. Furthermore, the competition experiments were utilized to continue exam the obstruct of the inclusion complexes nanofibrous membrane in the detecting F- from the other anions. Under the same condition, 100 μmol L-1 F- was first introduced in the inclusion complexes nanofibrous membrane to induce fluorescence decrease , then 1 mmol L-1 Cl-,Br-, I-, CN-, HSO4-, H2PO4-, AcO-, NO3-, ClO4-, PO43-, SO42-, HPO42-, HS- were introduced into the fluorescence-attenuated mixed system respectively. As illustrated in the red bar of Figure 4, the F- still resulted in the similar fluorescence changes, so it was convinced that these anions did not interference the detecting for F-. For rationalizing the good selectivity of the inclusion complexes nanofibrous membrane in detecting F-, we think the acceptor moieties distributed on the surface of nanofibrous membrane possess stronger binding capacity for F-, the binding mode blocks the excited state electrons from moving back to emit fluorescence, but for the other anions, their entries are not provided with these traits to decrease the fluorescence,therefore this causation brings out the favorable selectivity of the inclusion complexes nanofibrous membrane to F-. [2121 ZHOU, C., ZHANG, Y.N., LIU, H., “A novel nanofibrous film chemosensor for detecting and adsorbing Fe3+”, Journal of the Brazilian Chemical Society, v. 29, n. 3, pp. 457-462, Mar. 2018.].

C e q e   =   1 K L q m   +   C e q m (2)

In the equation, qe represents the equilibrium quantity of F- adsorbed in the inclusion complexes nanofibrous membrane, Ce represents the equilibrium concentration, qm represents saturation adsorption capacity and KL represents binding energy, thereinto, qm and KL are related to the Langmuir constants. As illustrated in Figure 8b Ce qe-1 and Ce were in a linear relationship (R2 > 0.99). According to the Langmuir theory, every single receptor only absorbed one donor, so the adsorption appears in the inclusion complexes nanofibrous membrane is monoptychial.17 Thus the F- adsorption capacity could be calculated from linear equation between Ce qe-1 and Ce in Figure 8b, and it is 16.67 mg/g of the inclusion complexes nanofibrous membrane to F- (Table 1).

Figure 8
Adsorption isotherm plot of F- on the inclusion complexes nanofibrous membrane (a) and Langmuir plot of F- on the inclusion complexes nanofibrous membrane (b)
Table 1
The Langmuir constants for F- on the inclusion complexes nanofibrous membrane

5. CONCLUSION

In conclusion, we have fabricated functionalized inclusion complexes nanofibrous membrane via electrospinning and host-guest interaction, the identification groups on the surface of the membrane afford the fluorescent sensor good sensitivity and selectivity for F-,in addition, the porous reticulation structure with large specific surface area offers the nanofibrous membrane good adsorption ability for F-. We believe these unique advantages make the fluorescent sensor have potential application value in the future.

ACKNOWLEDGMENTS

The authors gratefully acknowledge the support of Jilin Provincial Department of Science and Technology Outstanding Youth Talent Fund Project (20190103036JH), Jilin Provincial Education Department "the 13th Five-Year Plan" Science and Technology Research Project (JJKH20181115KJ and JJKH20200738KJ), Undergraduate Entrepreneurship Project of Changchun University of Science and Technology, and the Youth Fund Project of Changchun University of Science and Technology (XQNJJ-2019-12).

BIBLIOGRAPHY

  • 1
    YANG, L., DONG, T., REVANKAR, H. M., et al, “Recent progress on fluorination in aqueous media”, Green Chemistry, v. 19, n. 17, pp. 3951-3992, Jul. 2017.
  • 2
    WANG, L.T., XIE, Y.H., YANG, J.L., et al, “Insight into mechanisms of fluoride removal from contaminated groundwater using lanthanum-modified bone waste”, RSC Advances, v. 85, n.7, pp. 54291-54305, Nov. 2017.
  • 3
    RAN, X., GAO, Q.Q., ZHANG, Y., et al., “Colorimetry and phase transition characteristics in sensing fluoride anion based on hydrazide organogelators”, RSC Advances, v. 88, n.7, pp. 56016-56022, Dec. 2017.
  • 4
    ALLED, M., FERNANDEZ, A., EDLER, K.J., et al, “Azulene–boronate esters: colorimetric indicators for fluoride in drinking water”, Chemical Communications, v. 53, n.93, pp. 12580-12583, Nov. 2017.
  • 5
    TURAN, I.S., SEVEN, O., AYAN, S., et al, “Amplified chemiluminescence signal for sensing fluoride ions”, ACS Omega, v. 7, n. 2, pp. 3291-3295, Jul. 2017.
  • 6
    WINCK, A.L., SANTOS, J.C.V., LENZ, D.M., et al, “Development and characterization of gas sensors using thin films of polyaniline as active layer”, Revista Materia, v. 23, n. 4, pp. 12259-12268, Sep. 2018.
  • 7
    YANG, T., HOU, P., ZHENG, L.L., et al, “Surface-engineered quantum dots/electrospun nanofibers as a networked fluorescence aptasensing platform toward biomarker”, Nanoscale, v. 43, n. 9, pp. 17020-17028, Nov. 2017.
  • 8
    CHANDRAN, G.T., LI, X.W., Ogata, A., et al., “Electrically transduced sensors based on nanomaterials (2012-2016)”, Analytical Chemistry, v. 89, n. 1, pp. 249-275, Jan. 2017.
  • 9
    RICHARDSON, J., CUI, J.W., BJORNMALM, M., et al, “Innovation in layer-by-layer assembly”, Chemical Reviews, v. 116, n. 23, pp. 14828-14867, Dec. 2016.
  • 10
    LU, C.L., XU, Z.C., CUI, J.N., et al., “Ratiometric and highly selective fluorescent sensor for cadmium under physiological pH range: a new strategy to discriminate cadmium from zinc”, Journal of Organic Chemistry, v. 72, pp. 3554-3557, Apr. 2007.
  • 11
    WANG, W., WANG, X.L., YANG Q.B., et al, “A reusable nanofibrous film chemosensor for highly selective and sensitive optical signaling of Cu2+ in aqueous media.”, Chemical Communications? v. 49, n. 42, pp. 4833-4835, Apr. 2013.
  • 12
    WANG, W., WONG, N.K., SUN, M.D., et al, “Regenerable fluorescent nanosensors for monitoring and recovering metal ions based on photoactivatable monolayer self-assembly and host-guest interactions”, ACS Applied Materials and Interfaces, v.7, n. 16, pp. 8868-8875, Apr. 2015.
  • 13
    BIAN, Q., WANG, W.S., WANG, S.T., et al “Light-triggered specific cancer cell release from cyclodextrin/azobenzene and aptamer-modified substrate”, ACS Applied Materials & Interfaces, v. 40, n. 8, pp. 27360-27367, Oct. 2016.
  • 14
    LIU, B., TIAN, H., “A selective fluorescent ratiometric chemodosimeter for mercury ion”, Chemical Communications, v. 25, n. 7, pp. 3156-3158, Jul. 2005.
  • 15
    ZHOU, C., LIU, H., “A novel nanofibrous film chemosensor for highly selective and sensitive optical signaling of Zn2+”, Journal of the Brazilian Chemical Society, v. 28, n. 10, pp. 1947-1952, Oct. 2017.
  • 16
    MIN, M.H., WANG, X.F., CHEN, Y.M., et al, “Highly sensitive and selective Cu2+ sensor based on electrospun rhodamine dye doped poly(ether sulfones) nanofibers”, Sensors and Actuators B: Chemical, v. 188, n. 7, pp. 360-366, Nov. 2013.
  • 17
    JIAO, S., WANG, X.C., SUN, Y.H., et al, “A novel fluorescein-coumarin-based fluorescent probe for fluoride ions and its applications in imaging of living cells and zebrafish in vivo”, Sensors and Actuators B, v. 262, pp. 188-194, Jun. 2018.
  • 18
    CHANDRAN, G.T., LI, X.W., OGATA, A., et al “Electrically transduced sensors based on nanomaterials (2012-2016)”, Analytical Chemistry, v. 89, n. 1, pp. 249-275, Nov. 2017.
  • 19
    ZHAO, Y., JIANG, C., HU, C., et al “Large-scale spinning assembly of neat, morphology-defined, graphene-based hollow fibers”, ACS Nano, v. 7, n. 3, pp. 2406-2412, Feb. 2013.
  • 20
    SAEED, K., HAIDER, S., OH, T.J., et al, “Preparation of amidoxime-modified polyacrylonitrile (PAN-oxime) nanofibers and their applications to metal ions adsorption”, Journal of Membrane Science, v. 322, n. 2, pp. 400-405, Sep. 2008.
  • 21
    ZHOU, C., ZHANG, Y.N., LIU, H., “A novel nanofibrous film chemosensor for detecting and adsorbing Fe3+”, Journal of the Brazilian Chemical Society, v. 29, n. 3, pp. 457-462, Mar. 2018.

Publication Dates

  • Publication in this collection
    24 May 2021
  • Date of issue
    2021

History

  • Received
    10 Dec 2019
  • Accepted
    02 Apr 2020
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