Nitrogen-doped carbon quantum dots as fluorescent probe for “off-on” detection of mercury ions, l -cysteine and iodide ions

Nitrogen-doped carbon quantum dots as fluorescent probe for “off-on” detection of mercury ions, l -cysteine and iodide ions

Journal of Colloid and Interface Science 506 (2017) 373–378 Contents lists available at ScienceDirect Journal of Colloid and Interface Science journ...

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Journal of Colloid and Interface Science 506 (2017) 373–378

Contents lists available at ScienceDirect

Journal of Colloid and Interface Science journal homepage: www.elsevier.com/locate/jcis

Short Communication

Nitrogen-doped carbon quantum dots as fluorescent probe for ‘‘off-on” detection of mercury ions, L-cysteine and iodide ions Hao Huang a,b, Yuhui Weng a, Lihao Zheng a,b, Bixia Yao a,b, Wen Weng a,b,⇑, Xiuchun Lin c,⇑ a

College of Chemistry and Environment, Minnan Normal University, Zhangzhou 363000, China Fujian Provincial Key Laboratory of Modern Analytical Science and Separation Technology, Zhangzhou 363000, China c College of Environmental and Engineering, Putian University, Putian 351100, China b

g r a p h i c a l a b s t r a c t An ‘‘off-on” method for highly sensitive and selective detection of Hg2+ and L-cysteine (L-Cys) or Hg2+ and I using home-made nitrogen-doped carbon quantum dots (N-CQDs) as fluorescent probe was reported.

a r t i c l e

i n f o

Article history: Received 7 May 2017 Revised 14 July 2017 Accepted 19 July 2017 Available online 20 July 2017 Keywords: Carbon quantum dots Fluorescent probe Mercury ions L-Cysteine Iodide ions

a b s t r a c t The application of fluorescent nanoparticles to the detection of inorganic ions and organic compounds has been attracted wide attention recently. In this paper, an ‘‘off-on” method for highly sensitive and selective detection of Hg2+ and L-cysteine (L-Cys) or Hg2+ and I using home-made nitrogen-doped carbon quantum dots (N-CQDs) as fluorescent probe was reported. The N-CQDs with a fluorescence quantum yield of 42.2% were prepared using tartaric acid, citric acid and ethanediamine as the precursors in the oleic acid media. The fluorescence of the obtained N-CQDs could be quenched selectively and sensitively by the addition of Hg2+ (turn-off) with a detection limit of 83.5 nM. When L-Cys or I was added into the N-CQDs-Hg2+ system, the fluorescence was recovered effectively (turn-on). This process could be used to the detection of L-Cys or I with a detection limit of 45.8 and 92.3 nM, respectively. Ó 2017 Elsevier Inc. All rights reserved.

1. Introduction The pollution of heavy metal ions has become a serious worldwide problem due to their severe risks to human health and the environment. As one of the most toxic heavy metals, mercury with the feature of strong toxicity and bioaccumulation can cause seri-

⇑ Corresponding authors at: College of Chemistry and Environment, Minnan Normal University, Zhangzhou, 363000, China (W. Weng); College of Environmental and Engineering, Putian University, Putian, 351100, China (X. Lin). E-mail addresses: [email protected] (W. Weng), [email protected] (X. Lin). http://dx.doi.org/10.1016/j.jcis.2017.07.076 0021-9797/Ó 2017 Elsevier Inc. All rights reserved.

ous human health problems even at very low concentration [1,2]. On the other hand, L-cysteine, as a small-molecular-weight biological thiol-containing amino acid, is essential in maintaining biological redox homeostasis. An abnormal level of L-Cys has been linked to many diseases, such as slow growth, liver damage, skin lesion, Alzheimer’s disease and cardiovascular disease [3–6]. It is also well-known that the content of iodine is directly related to human health [7]. Iodine deficiency could lead to some serious problems such as intellectual disability. Iodine excess could also cause the disease. It is of great necessity to develop rapid and user-friendly

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Fig. 1. The TEM image (A), the UV–vis and photoluminescence spectrum (B), and the excitation-dependent emission spectrum (C) of the N-CQDs. Inset of A, the size distribution of the N-CQDs. Inset of B, the photographs under illumination of white (left) and UV (365 nm, right) light.

method for the detection of mercury ions, L-cysteine and iodide ions. Recently, the application of fluorescent nanoparticles to the detection of inorganic ions and organic compounds, temperature sensing, bioimaging and nanomedicine has been attracted wide attention [8–12]. Various nanomaterials including fluorescently doped silicas and sol-gels, hydrophilic polymers (hydrogels), hydrophobic organic polymers, semiconducting polymers dots, quantum dots, carbon dots, other carbonaceous nanomaterials, upconversion nanoparticles, noble metal nanoparticles (mainly gold and silver), etc. have been investigated for these applications [13–16]. Among them, carbon dots have received particular concern because of their excellent optical properties, good biocompatibility, great aqueous solubility, and simple synthesis [17]. Heteroatom-doped carbon dots which often possess high fluorescent quantum yield have even become the focus. Xu et al. developed a new fluorescent probe based on ensemble of gold nanoclusters and polymer protected gold nanoparticles for turn-on sensing of L-cysteine [18]. Li et al. developed a simple and distinctive method for the ultrasensitive detection of Cu2+ and Hg2+ based on surface-enhanced Raman scattering using cysteinefunctionalized silver nanoparticles attached with Raman-labeling molecules [19]. Amjadi et al. investigated a carbon dots-silver nanoparticles fluorescence resonance energy transfer system as a novel turn-on fluorescent probe for selective determination of cysteine [20]. Lin et al. prepared europium-decorated graphene quantum dots as a novel ‘‘off-on” fluorescent probe for the label-free determination of Cu2+ and L-cysteine [21]. Developing convenient methods based on novel nanomaterials for the detection of metal ions and biological active substances is still of great significance. In this report, water-soluble N-CQDs prepared from tartaric acid, citric acid and ethanediamine by a facile one-pot solvothermal method were used to the ‘‘off-on” detection of Hg2+, L-Cys and I with high sensitivity and selectivity. The N-CQDs could be obtained conveniently, and the established method has a promising prospect for the detection of real samples. 2. Experimental 2.1. Chemicals Citric acid monohydrate (CA), tartaric acid, ethanediamine and oleic acid were all analytical reagents. They were purchased from Shanghai Sinopharm Chemical Reagent Co. Ltd. (China). Quinine sulfate (AR) was purchased from Aladdin Industrial Corporation (Shanghai, China). Ultrapure water was prepared with a Milli-Q system (Millipore, Bedford, MA, USA). Other reagents were all analytical and were used without further purification.

2.2. Characterization of the N-CQDs The fluorescence spectra were obtained by a Varian Cary Eclipse Fluorescence Spectrophotometer. Transmission electron microscopy (TEM) and high-resolution TEM (HRTEM) images were recorded using FEI Tecnai G2 F20 instruments. The X-ray photoelectron spectroscopy (XPS) spectra were recorded using a Thermo ESCALAB 250Xi multifunctional imaging electron spectrometer. A UV-2550 spectrophotometer was used to record the UV–vis spectra. A Magna-IR 750 Fourier transform infrared spectrometer (Nicolet) was used to record the FTIR spectra. The fluorescence decay experiments were performed using an Edingburgh Instruments FLS920 fluorescence spectrometer. 2.3. Preparation of the N-CQDs The N-CQDs were prepared according to a simple one-step solvothermal method reported by our group [22,23]. Typically, CA monohydrate (1.5 g) and tartaric acid (1.5 g) were placed in a three neck flask, and then ethanediamine (5 mL) and oleic acid (30 mL) were added. The mixture was heated at 220 °C for 30 min under vigorous magnetic stirring. The colorless solution changed to a clear brownish black solution as the reaction progressed. After the reaction, the solution was cooled at room temperature, and then black solid precipitate was obtained directly. The precipitate was washed sufficiently with n-hexane, dispersed in ultrapure water and centrifuged at 6000 rpm for 30 min to remove large particles product. 3. Results and discussion The N-CQDs were prepared by a facile solvothermal method with oleic acid as the reaction media. The product was then characterized by TEM, XPS, FTIR, UV–vis and photoluminescence spectrum. From the TEM image (Fig. 1A) we can find that the resulting product has good dispersion with a narrow size distribution in the range of 1 to 4 nm (inset of Fig. 1A). The average diameter of the NCQDs is about 2.66 nm. The obtained N-CQDs are amorphous as the HRTEM images do not show any discernible lattice fringes. There are two distinct absorbance bands centered at 239 and 351 nm (Fig. 1B). The peak at 239 nm can be ascribed to the p– p⁄ transitions of the aromatic C@C sp2 domains which cannot produce observed fluorescence signal [24,25]. The other absorption peak at 351 nm can be ascribed to the trapping of excited state energy of the surface states, which can lead to strong fluorescence [26,27]. The fluorescent spectrum for the obtained N-CQDs conformed to the UV–vis absorption features. Fig. 1C shows that the emission peak remains essentially unchanged with the variation

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Fig. 2. The FTIR spectrum (A) and the XPS spectrum (B) of the N-CQDs. (C) and (D) are the corresponding C1s spectrum and N1s spectrum.

of excitation wavelength in the range of 320–400 nm. With the further increase of excitation wavelength, a redshift of emission wavelength happened. The maximum emission peak was observed at 460 nm, at an excitation wavelength of 360 nm. The product emitted bright blue1 color under 365 nm UV light (Fig. 1B, inset). The fluorescence quantum yield of the obtained NCQDs was calculated to be 42.2% using quinine sulfate as a reference. The FT-IR spectrum (Fig. 2A) shows a broad band around 3403 cm 1, which can be attributed to NAH and OAH stretching vibrations. The intense peaks at 1654 and 1560 cm 1 can be assigned to asymmetric C@O and C@N stretching vibrations. The XPS spectrum (Fig. 2B) exhibits three peaks at 286.05, 399.87 and 532.34 eV, which can be assigned to C1s, N1s, and O1s, respectively. Besides, the C1s spectrum can be fitted into four peaks at 284.67, 285.32, 285.88 and 287.64 eV (Fig. 2C), showing the presence of four types of carbon bonds: sp2 C@C or sp3 CAC, CAN or CAO, sp2 NAC@N, and C@O. The fitting of the N1s spectrum showed that there existed three types of nitrogen bonds: CANAC (399.34 eV), NA(C)3 (399.82 eV), and CANAH groups (400.58 eV) (Fig. 2C) [28]. Above characterizations indicated that the obtained NACQDs have abundant functional groups such as hydroxyl and amino groups due to the relatively low carbonization temperature. These polar functional groups endowed the product with perfect water solubility. 3.1. Selectivity and sensitivity of Hg2+ detection The N-CQDs with a final concentration of 2.1 lg mL 1 was used to evaluate the selectivity towards various metal ions. Different 1 For interpretation of color in Fig. 1, the reader is referred to the web version of this article.

metal ions (including Cr6+, Cu2+, Ni2+, Co2+, Cd2+, Zn2+, Mg2+, Sr2+, Pb2+, Ba2+, Al3+, K+, Na+, Fe2+, and Hg2+) were added into the NCQDs solution with a final concentration of 100 lM, then the FL spectra were recorded under excitation at 360 nm to study the selectively. Fig. 3A shows that the FL intensity decreases remarkably with the addition of Hg2+, whereas other ions had negligible or less impact on the intensity. This indicates that the obtained N-CQDs have high selectivity towards Hg2+ ions. In another control experiment, 30 lM of Hg2+ alone (red bars, Fig. 3B) and the mixtures of 30 lM of Hg2+ and 30 lM of the above mentioned metal ions (blue bars, Fig. 3B) were added into the NCQDs aqueous solution respectively, then the quenching effects were examined. The interference tests show that the coexistence of other ions only has a small or negligible effect on the fluorescence quenching. The concentration experiment (Fig. 3C and D) shows that the FL intensity decreases with the increase of Hg2+ concentration. There exists a good linear relationship (R2 = 0.9979) between the FL intensity and Hg2+ concentration in the range of 0–18 lM. The limit of detection (LOD) was estimated to be 83.5 nM based on three times the standard deviation rule. It should be noted that the obtained LOD of the as-prepared N-CQDs for Hg2+ detection is much lower or comparable to those previously reported with other fluorescent probes [12,29–31]. The results show that the as-prepared N-CQDs may be useful in environmental applications for Hg2+ detection. The method was then used to assay the concentration of Hg2+ in real water samples. The tap water samples obtained from our lab without any pretreatment were spiked with Hg2+ at different concentration levels and then analyzed with the proposed method. Similarly, the FL intensity decreased with increasing the concentration of Hg2+ in tap water. Good linear relationship between the PL

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Fig. 3. (A) Normalized fluorescence intensity of aqueous N-CQDs solution in the presence of various metal ions. (B) Interference experiments of aqueous N-CQDs solution towards Hg2+ (black bars) and other metal ions (red bars). (C) The dependence of FL intensity on the concentration of Hg2+ in the range of 0–30 lM. (D) The overlay fluorescence spectra of the N-CQDs solution upon addition of various concentrations of Hg2+ (from top to bottom: 0, 0.5, 1, 3, 6, 9, 12, 15 and 18 lM). (For interpretation of the references to colour in this figure legend, the reader is referred to the web version of this article.)

intensity and the concentration of Hg2+ ions was observed in the range of 0–18 lM. The sensitivity and selectivity for Hg2+ ions towards quenching of fluorescence of the N-CQDs are possibly due to several reasons, such as greater affinity of Hg2+ ions towards nitrogen, larger radius of Hg2+ ions and its ability to form a stable non-fluorescent complex with the N-CQDs [32]. Another possible explanation is aggregate-induced quenching [29]. The Hg2+ ion may simultaneously bind to multiple nitrogen and oxygen atoms of the N-CQDs. This complexation process may induce the formation of aggregates, change the electronic structure of the N-CQDs and then lead to non-radiative electron/hole recombination annihilation.

that the N-CQDs-Hg2+ sensor is insensitive to other amino acids but selective to L-Cys in the mixtures. As shown in Fig. 4B, the FL intensity of the N-CQDs-Hg2+ at 460 nm increases gradually with the increase of L-Cys concentration, indicating that addition of L-Cys can effectively recover the fluorescence of the N-CQDs-Hg2+. Fig. 4C shows the effect of the amount of L-Cys on the fluorescence recovery of the system. It can be seen that the enhancement of fluorescence is proportional to the concentration of L-Cys in the range of 0 to 40 lM (R2 = 0.9990). The limit of detection (LOD) was estimated to be 45.8 nM based on three times the standard deviation rule. This sensitivity is higher than that of other reported methods [18,21,34]. The good repeatability of the sensing system can also be observed from the calculated error bars.

3.2. Detection of L-Cys 3.3. Detection of I It is reported that L-Cys could react with Hg2+ due to the existence of thiol group [19,33]. The Hg2+-S bond would be formed in the process. Thus, Hg2+ would be removed from the surface of the N-CQDs and the fluorescence intensity would be recovered due to avoidance of fluorescence quenching by Hg2+ species. Therefore, the N-CQDs-Hg2+ system was explored to probe L-Cys. We found that the quenched fluorescence of the N-CQDs was recovered immediately upon the addition of L-Cys to the solution of NCQDs-Hg2+. The fluorescence signal stabilized after 1 min, indicating a fast recovery of the system. Several relevant amino acids including L-Cys, L-Ser, L-Tyr, D-Asp, L-Trp, D-Trp, L-Phe and D-Phe showed only a small or negligible recovering effect. In the control experiment, 30 lM of L-Cys alone (black bars, Fig. 4A) and the mixtures of 30 lM of L-Cys and 300 lM of the above mentioned amino acids (red bars, Fig. 4A) were added into the N-CQDs-Hg2+ aqueous solution respectively. Then the FL recovering effects of L-Cys and the mixtures of L-Cys and other amino acids on the N-CQDs-Hg2+ were examined. The results showed that the influence of other coexisting amino acids was negligible. These observations indicate

It was reported that iodide ions can also be effectively bound to Hg2+ to form the Hg2+-I complex. Thus, Hg2+ may be removed from the N-CQDs-Hg2+, which makes the fluorescence increase due to avoidance of fluorescence quenching from Hg2+ species [30,32]. Various environmentally relevant anions, including Br , Cl , F , SO24 , C2O24 , Ac , CO23 , HCO3 , PO34 and I , were added into the N-CQDs-Hg2+ solution. Significant FL recovering effect was observed with the addition of I , while other anions showed no or only a slighter recovered effect. In the control experiment, 90 lM of I alone (black bars, Fig. 5A) and the mixtures of 90 lM of I and 900 lM of the above mentioned anions (red bars, Fig. 5A) were added into the N-CQDs-Hg2+ aqueous solution respectively, then the FL recovering effects of I and the mixtures of I and other anions on the fluorescence of the N-CQDs-Hg2+ were examined. The results clearly show that the influence of other coexisting anions on the FL recovering effect is negligible. These observations further indicate that the N-CQDs-Hg2+ sensor is selective to I in the mixtures.

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Fig. 4. (A) FL intensity of aqueous N-CQDs-Hg2+ solution towards 30 lM L-Cys (black bars), and interference of 300 lM of other amino acids (red bars). (B) The dependence of FL intensity of N-CQDs-Hg2+ on the concentrations of L-Cys in the range of 0–70 lM. (C) The overlay fluorescence spectra of the N-CQDs-Hg2+ solution upon addition of various concentrations of L-Cys. (For interpretation of the references to colour in this figure legend, the reader is referred to the web version of this article.)

Fig. 5. (A) FL intensity of aqueous N-CQDs-Hg2+ solution towards 90 lM I (black bars), and interference of 900 lM of other anions (red bars). (B) The dependence of FL intensity of N-CQDs-Hg2+ on the concentrations of I in the range of 0–110 lM. (C) The overlay fluorescence spectra of the N-CQDs-Hg2+ solution upon addition of various concentrations of I . (For interpretation of the references to colour in this figure legend, the reader is referred to the web version of this article.)

Fig. 5B shows the effect of the amount of I on the fluorescence recovery of the system. It can be seen that the fluorescence intensity of the system increases with the increase of I concentration. Fig. 5C shows the effect of the amount of I on the fluorescence recovery of the system. The enhancement of fluorescence is proportional to the concentration of I in the range of 0–90 lM (R2 = 0.9962). The limit of detection (LOD) was estimated to be 92.3 nM based on three times the standard deviation rule. This sensitivity is higher than that of other reported methods [35–37]. The good repeatability of the sensing system for the detection of I can be observed from the calculated error bars. Though the mechanism of ‘‘off-on” fluorescence for the obtained N-CQDs was not entirely clear at this point, some characterizations have been performed in order to deepen the understanding of this process. The UV–vis spectral analysis showed that the UV–vis spectra had no significant change when Hg2+ ions were added into the N-CQDs aqueous solutions. The intensity and position of the absorbance bands centered at 239 and 351 nm did not change nearly. Besides, the fluorescence decay experiments showed that the fluorescence life time of the N-CQDs decreased obviously in the process of fluorescence quenching with Hg2+ ions (from 15.5 ns to 11.2 ns). These results indicated that the fluorescence quenching belonged to dynamic quenching process, and electron transfer process between the excited states of the NCQDs with Hg2+ ions may be the main reason for fluorescence quenching. When L-Cys or I was added into the N-CQDs-Hg2+ system, the UV–vis spectra mainly reflected the feature of Hg2+-L-Cys or Hg2+-I complexes. So we deduced that Hg2+ ions can be effectively carried off from the surface of the N-CQDs by L-Cys

or I , and then the fluorescence of the N-CQDs was retrieved.

4. Conclusions In conclusion, we have prepared highly fluorescent N-CQDs with a quantum yield of 42.2% via a facile one-pot solvothermal method. The as-prepared N-CQDs have been successfully used for ‘‘off-on” detection of Hg2+ and L-Cys or Hg2+ and I with high sensitivity and selectivity. Hg2+ can effectively quench the fluorescence of the obtained N-CQDs through the charge transfer process. Upon the addition of L-Cys or I into N-CQDs-Hg2+, the fluorescence can be recovered. The possible mechanism relies upon LCys or I being able to effectively shelter the quenching due to the binding of Hg2+ and L-Cys or I , which removes Hg2+ from the surface of the N-CQDs. Detection limits of 83.5 nM for Hg2+, 45.8 nM for L-Cys, and 92.3 nM for I were achieved. The established method has a promising prospect for the detection of real samples. Acknowledgements This work was supported by Natural Science Foundation of Fujian Province of China (Nos. 2016Y0065 and 2014J01053), Education Bureau of Fujian Province of China (Nos. JA13195 and JK2011030), and the College Students’ Innovative and Entrepreneurial Training Program (Nos. 201710402023 and 201710402071). References [1] E.M. Nolan, S.J. Lippard, Tools and tactics for the optical detection of mercuric ion, Chem. Rev. 108 (2008) 3443–3480. [2] F. Zahir, S.J. Rizwi, S.K. Haqb, R.H. Khan, Low dose mercury toxicity and human health, Environ. Toxicol. Pharma. 20 (2005) 351–360.

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