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Article

The Trace Detection of Nitrite Ions Using Neutral Red Functionalized SH-β-Cyclodextrin @Au Nanoparticles

by
Xiaoyang Du
1,
Xiaoxia Zhang
1,
Chunlai Jiang
3,
Weilu Zhang
1,* and
Lizhu Yang
2,*
1
College of Chemistry & Materials Engineering, Wenzhou University, Wenzhou, Zhejiang 325035, China
2
School of Pharmaceutical Sciences, Wenzhou Medical University, Wenzhou, Zhejiang 325035, China
3
The Atmospheric Environment Department, Chinese Academy for Environmental Planning, Beijing 100012, China
*
Authors to whom correspondence should be addressed.
Sensors 2018, 18(3), 681; https://doi.org/10.3390/s18030681
Submission received: 28 December 2017 / Revised: 9 February 2018 / Accepted: 21 February 2018 / Published: 25 February 2018
(This article belongs to the Special Issue Fluorescent Probes and Sensors)
Browse Figures
Versions Notes

Abstract

:
A novel fluorescence sensor of NR-β-CD@AuNPs was prepared for the trace detection of nitrite in quantities as low as 4.25 × 10−3 μg∙mL−1 in an aqueous medium. The fluorescence was due to the host-guest inclusion complexes between neutral red (NR) molecules and gold nanoparticles (AuNPs), which were modified by per-6-mercapto-beta-cyclodextrins (SH-β-CDs) as both a reducing agent and a stabilizer under microwave radiation. The color of the NR-β-CD@AuNPs changed in the presence of nitrite ions. A sensor was applied to the determination of trace nitrites in environmental water samples with satisfactory results.

1. Introduction

Gold nanoparticles (AuNPs) have important applications in the fields of nanoscience and nanotechnology because of their unique optical, electronic, and catalytic properties [1]. First, the distance-dependent surface plasmon resonance (SPR) band of AuNPs makes them vital units for establishing assembly/disassembly modulated colorimetric sensors [2,3]. Second, the high specific surface areas of AuNPs result in their surfaces being modified with multiple ligands [4]. Meanwhile, AuNPs are an ideal energy acceptor in structured fluorescence resonance energy transfer systems (FRET) due to their high extinction coefficient [5,6,7]. Additionally, the major advantage of AuNPs-based sensors is that the molecular recognition can appear as a color change, which can be easily observed by the naked eye [8]. To date, AuNPs have been applied to the fabrication of assembly/disassembly modulated colorimetric sensors [9], as well as various types of optical [10,11] and electrochemical [12,13] sensors and biosensors [14]. Among them, the interactions of AuNPs with macrocycles such as cyclodextrins, calixarenes, and cucurbiturils [15,16,17] have received considerable attention for their special and potential properties, for example, the application of resveratrol-stabilized AuNPs in the anticancer field [18].
As a well-known molecular receptor, β-cyclodextrin (β-CD) can form host-guest inclusion complexes with a wide variety of organic, inorganic, and biologic guest molecules in their hydrophobic cavities [19,20]. In parallel, β-CD is water-soluble and environmentally friendly, and is useful in improving the dispersibility of the functional materials [21,22,23,24]. On the basis of host-guest interactions, these complexes have been well applied to self-assembly, drug/gene delivery, separation, and sensing applications [15,25]. Considering the unique topological structures that macrocyclic supramolecules possess, several novel3452 properties and corresponding new applications may be presented when β-CD is attached to the surfaces of AuNPs [26]. For example, β-CD-capped AuNPs assembled on ferrocene-functionalized indium tin oxide surfaces were applied to enhance the voltammetric analysis of ascorbic acid [27].
The concentration of NO2− is one of the most important parameters in water quality [28]. The maximum allowable amount of nitrite in drinking water is 100 ng·mL−1, according to the regulation of the European Community [29]. The rapid detection of trace concentrations of NO2− in water bodies is essential [30,31]. Many analytical methods for the trace detection of nitrite and nitrate have been reported, including colorimetric methods [32,33], fluorometric methods [34], and electrochemical methods [35,36]. However, these methods have limitations such as poor sensitivity, anti-interference, and the use of expensive experimental apparatus. The chemiluminescent methods have proven to be more sensitive and selective in the measurement of nitrite and nitrate [37,38,39,40,41,42]. Some of the typical methods are summarized in Table S1 (see Supplementary materials). Neutral red (NR) exists in two different prototropic forms in aqueous solutions, namely, the cationic/protonated (NRH+) and neutral (NR) forms, depending on the pH of the solution. NR is a type of dye containing a primary amine structure, which can interact with NO2− and lead to fluorescence quenching. Meanwhile, it has been reported that hydroxyls in the cavities of β-CD form inclusion complexes with the nitrogen atoms on heterocyclic molecules of NR [43,44].
In this paper, a sensitive sensor is established for the trace detection of NO2− in water because of the observation of a color change. Ultraviolet–visible spectroscopy (UV-Vis), transmission electron microscopy (TEM), and Fourier transform infrared spectroscopy (FT-IR) spectra are explored to understand the quenching interaction and corresponding binding forces. AuNPs modified by SH-β-CD were used as both the reducing agent and stabilizer in this method. Monodispersed β-CD@AuNPs with 10 nm diameters are synthesized in an eco-friendly way, which is different than previous approaches used for the fabrication of β-CD@AuNPs [45,46]. No harsh reagents are used in this method. NR-β-CD@AuNPs were synthesized by host-guest recognition between the β-CD@AuNPs and NR. The host was β-CD@AuNPs, and the guest was NR. The detection of nitrite ions was traced by the diazonium reaction of NO2− and the primary amine of NR. The fabrication of the NR-β-CD@AuNP sensor and nitrite detection are shown in Scheme 1.

2. Materials and Methods

2.1. Reagents and Materials

Chloroauric acid trihydrate (HAuCl4·3H2O, 99.99%), sodium nitrite (NaNO2, 99.0%), hydrochloric acid (HCl, 36%), borax (Na2B4O7·10H2O, 99.0%), sodium bicarbonate (Na2CO3, 99.0%), neutral red (NR, 4% in water), sodium bicarbonate (NaHCO3, 99.0%), disodium hydrogen phosphate (Na2HPO4, 99.0%), sodium sulfate (Na2SO4, 99.0%), sodium chloride (NaCl, 99.0%), sodium fluoride (NaF, 99.0%), sodium dihydrogen phosphate (NaH2PO4, 99.0%), and sodium nitrate (NaNO3, 99.0%) were purchased from Aladdin Industrial Corporation (Shanghai, China). Per-6-mercapto-beta-cyclodextrin (SH-β-CD, 99.0%) was purchased from Shandong Binzhou Zhiyuan Bio-Technology Co., Ltd (Shandong, China). Other reagents were of analytical grade and directly used without further purification. All solutions were prepared using ultra-pure water (=18.20 MΩ·cm).

2.2. Apparatus

The morphology and the size of products were obtained from TEM, JEM-2100 (JEOL, Tokyo, Japan). The absorption spectra were obtained using a UV-2600 spectrophotometer (SHIMADZU, Tokyo, Japan). The fluorescence spectra were obtained using a FluoroMAX-4-TCSPC detector (HORIBA Jobin Yvon, Paris, France). The AuNPs were prepared with the microwave reactor Discover CEM (CEM, Matthews, NC, USA).

2.3. Preparation of the SH-β-CD Functionalized AuNPs (β-CD@AuNPs)

The β-CD@AuNPs were synthesized by the SH-β-CD reduction of HAuCl4. Briefly, 0.010 g HAuCl4·3H2O and 15.0 mg SH-β-CD were dissolved in 30.0 mL ultra-pure water using an ultrasonication for 5 min. The mixture was stirred for 3 min at 120°C under microwave radiation of 150 W. A suspension of the β-CD@AuNPs characterized by a wine-red color was finally obtained and stored at 4 °C. The reaction was different from previous approaches for the preparation of β-CD@AuNPs because no sodium borohydride was used.

2.4. Preparation of Fluorescence Dye-Incorporated SH-β-CD Functionalized Gold Nanoparticles (NR-β-CD@AuNPs)

In a typical experiment, 5 mL of a NaHCO3-borax buffer solution and 5 mL of NR (5 × 10−6 mol·L−1) were added into 5 mL of the β-CD@AuNP solution, and the solution was stirred in a dark environment at room temperature for 80 min. A solution of NR-β-CD@AuNPs was obtained, which became orange-red.

2.5. Detection of Nitrite Ions

NaNO2 (14.99 mg) was dissolved in ultra-pure water to prepare a 100.0 mg·L−1 standard solution, which was diluted to the desired concentrations for further use. A NaNO2 standard solution (2.1 mL) and a HCl (1.50 mg·L−1) solution (0.2 mL) were added sequentially into a 5-mL colorimetric tube, followed by the addition of 0.7 mL of the above-prepared NR-β-CD@AuNP solution. Fluorescence spectra were obtained after 5 min.

2.6 Detection of Nitrite Ions in Real Samples

The water samples were obtained from local ponds and Oujiang river (Wenzhou City, China). Then, the samples underwent filtration and centrifugal separation, after which the NR-β-CD@AuNPs were added to the samples, and then the fluorescence spectra were collected.

3. Results

3.1. Characterization of the β-CD@AuNPs

The UV-Vis spectra of the β-CD@AuNPs are shown in Figure 1A. An absorption band at 526 nm indicated the typical feature of the AuNPs and the localized surface plasmon resonance of the dispersed β-CD@AuNPs. The absorption peak was sharper than that prepared from HAuCl4 reduced by sodium citrate (see Supplementary materials, Figure S1A). The color also exhibited a slight variation that can be seen from the inner illustration of Figure 1A. The different colors of the AuNPs obtained using SH-β-CD and sodium citrate may be due to their different sizes and morphologies, as mentioned in Reference [47]. When the surfaces of the AuNPs were decorated with SH-β-CD molecules, they could be employed as scaffolds and energy acceptors for fluorescent sensing by host-guest interactions. The binding of SH-β-CD with AuNPs was verified by comparing the FT-IR spectra between the SH-β-CDs and β-CD@AuNPs, as shown in Figure 1B. The spectrum of SH-β-CD (b) had a band at 1647 cm−1 that corresponds to the stretching vibration peak of -C=O. The bands at 1157 and 938 cm−1 correspond to the stretching vibration peak of -C-O. The peak at 1590 cm−1 of the spectrum of β-CD@AuNPs (a) is the stretching vibration peak of -C=O. The two peaks at approximately 1155 and 1028 cm−1 correspond to the stretching vibration peak of -C-O. Moreover, the S-H stretching band at 2576 cm−1 of SH-β-CD (b) disappeared in the FT-IR spectrum of β-CD@AuNPs (a), which proved the formation of an Au-S bond, according to References [8] and [26].
To further confirm their nanostructure and atomic composition, the β-CD@AuNPs were analyzed by transmission electron microscopy (TEM), and the images are shown in Figure 2. The β-CD@AuNPs were nearly spherically shaped with an average size of 10 nm. Energy dispersive spectrometry (EDS) element mappings of β-CD@AuNPs are also shown in Figure 2 using different colors, in which the red and green areas correspond to elemental Au and S, respectively.
The preparation of AuNPs from HAuCl4 reduced by sodium citrate was also tested in this paper. Additionally, the morphological characteristics of the TEM images are shown in Figure S1B (see Supplementary materials). Several of the nanoparticles were approximately 10 nm in size and some exhibited an irregular spherical shape.

3.2. Characterization of the NR-β-CD@AuNPs

To demonstrate the potential application of NR-β-CD@AuNPs during the trace detection of NO2− in water, the host-guest recognition of β-CD@AuNPs and NR molecules was studied in this paper. Nitrogen heterocyclic molecules reacted with the hydroxyls of β-CD when the guest molecules of NR entered the cavities of the β-CD@AuNPs, used as the host molecules. The AuNPs were designed especially for their signal amplification in this paper. Therefore, a sensor of NR-β-CD@AuNPs exhibits a higher sensitivity than a sensor of both NR and NR-β-CD (see Supplementary materials, Figure S2A). The fluorescence of the NR-β-CD@AuNPs were gradually quenched with the addition of the host molecules of β-CD@AuNPs, and ultimately a stable quenching rate was attained when the volume of the β-CD@AuNPs was 5 mL. The fluorescence spectra are shown in Figure 3A. The relationship between fluorescence intensity and the volume of the β-CD@AuNPs solution is shown in Figure 3B. The fluorescence intensity of the NR-β-CD@AuNPs gradually decreased with an increase in β-CD@AuNPs. The fluorophores entered into the macrocyclic cavities of the β-CD@AuNPs for structure matching by host-guest interactions. As a consequence, the quenching efficiency achieved a constant value when the volume of the β-CD@AuNPs solution reached 5 mL. The average size of the NR-β-CD@AuNPs was 10 nm (see inserted TEM image in Figure 3B) and the dispersion of size was even and comparable to that of the β-CD@AuNPs (shown in Figure 2).
The energy of NR was transferred to the AuNPs through β-CD during the synthesis of NR-β-CD@AuNPs [47]. The quenching constant of Ksv was 1.68 × 104 L·mol−1, which was calculated according to the Stern-Volumer equation [48]:
F / F 0 = 1 + K S V [ Q ]
where F0 and F are the fluorescence intensities before and after the addition of β-CD@AuNPs, respectively; Ksv is the static quenching constant; and [Q] is the concentration of β-CD@AuNPs.

3.3. Effect of pH on the Fluorescence Property of the NR-β-CD@AuNPs

The prototropic equilibrium shifted from NRH+ to NR in the cavity of SH-β-CD with a change in the solution pH. NRH+ was the main form in an acidic aqueous solution with an absorption peak at 530 nm, and NR was the dominant form in a weakly alkaline media with an absorption peak at 450 nm. The fluorescence spectra of the NR-β-CD@AuNPs were changed with various pH values accordingly to the reaction between the NR-β-CD@AuNPs and NO2−, which could be clearly monitored by the fluorescence spectra. A diazonium group was formed by the selective reaction between NO2− and the primary amine group of NR, which is unstable in weakly acidic and alkaline media, and rapidly converted to another stable form with nitrogen (N2) released [49]. On the other hand, diazonium salts easily react with surplus aromatic amine groups in NR with a deficiency of NO2− during the diazotization reaction. As a result, the acid-base properties of the solution and the concentrations of NO2− were the principal factors for the diazo coupling reaction.
Experiments were carried out to explore the fluorescence properties of NR-β-CD@AuNPs at different pH values in the range of 2–9. The effect of pH on the excitation spectra of the NR-β-CD@AuNPs is shown in Figure 4A. The excitation peak appeared at 448 nm when the solution was weakly alkaline, which corresponds to the neutral form of NR. Another excitation peak appeared at 532 nm (pH = 7) due to the increasing amount of the protonated form of NRH+. Only the excitation peak at 532 nm remained when the aqueous solution was acidic. The corresponding emission peak (red line) shifted from 621 to 627 nm with an increase in the fluorescence intensity in Figure 4B. Because the ground-state pKa value was 6.8 of NR in water, the critical point of the excitation peak at pH = 7 appeared. Changing from rose-red to purple, the colors of the NR-β-CD@AuNPs were different in weakly alkaline and acidic solutions, as shown in the inserted image of Figure 4B. The TEM image in Figure 4C shows the morphology of the NR-β-CD@AuNPs at pH 5, which is similar to that at pH 9. In the presence of NO2−, the fluorescence intensity of the solution clearly decreased compared to that of the NR-β-CD@AuNPs solution, as shown in Figure 4C. The NR-β-CD@AuNPs can detect trace amounts of NO2− in acidic to weakly alkaline aqueous solutions. It was demonstrated that NR-β-CD@AuNPs have a broad detection range. The relatively wide detection range of NR-β-CD@AuNPs may have contributed to the structure of β-CD@AuNPs.

3.4. The Detection of NO2− in an Aqueous Solution

To investigate the detection sensitivity of NR-β-CD@AuNPs to NO2− in broad ranges, experiments were designed in both weakly alkaline and acidic media. When the solution was weakly alkaline, the fluorescence intensity of the NR-β-CD@AuNPs at 623 nm was clearly gradually quenched with an increasing concentration of NO2− ([NO2−]), as shown in Figure 5A. A linear relationship (R2 = 0.998) was obtained between the fluorescence intensity and [NO2−] in the range of 0.0–0.9 μg·mL−1. When [NO2−] exceeded 0.9 μg·mL−1, the rate of fluorescence quenching reached 100%, and the color changed accordingly. The regression equation was F = 473893 − 539242C, where F represents the fluorescence intensity of the solution, and C represents [NO2−] (see Supplementary materials, Figure S3A). The detection limit was as low as 5.78 × 10−3 μg·mL−1, which was calculated as follows: the blank solution was measured 11 times, and its standard deviation was multiplied by 3 and divided by the slope of the linear relationship. The fluorescence quenching was static because the non-fluorescent diazonium groups were produced, and Ksv was 9.8 × 104 L·mol−1, as calculated by Equation (1). The experiments under acidic conditions were performed in the same way as those performed under weakly alkaline conditions, apart from the employed pH values, and the results are shown in Figure 5B. The regression equation was F = 574156 − 673222C (see Supplementary materials, Figure S3B), and the detection limit was 4.25 × 10−3 μg·mL−1, which is better than that of the weakly alkaline conditions. The Ksv was 2.1 × 105 L·mol−1, as determined by Equation (1).
As shown in Figure 6, the colorimetric response was recorded. It was obvious that the color changed from light purple to light blue, and could be observed by the naked eye, when [NO2−] was approximately 0.30 μg·mL−1.
Both NR and NR-β-CD could be used to detect NO2− based on our results (see Supplementary materials, Figure S4), and the detection limit was 0.56 μg·mL−1 and 5.6 × 10−2 μg·mL−1, respectively. The solutions must be under a strongly acidic condition of pH 1 for higher detection limits. The NR-β-CD@AuNP sensor exhibited a good sensitivity of 5.78 × 10−3 μg·mL−1.
The diazonium group between NO2− and the primary amine group of NR was more stable in an acid solution [49]. Compared with other sensors [50,51], this sensor displayed a wide detection range and good sensitivity. Some of the typical methods are summarized in Table S1 (see Supplementary materials).
After reacting with NO2−, the product of NO2-NR-β-CD@AuNPs was analyzed by UV-Vis spectra (Figure 7). The UV-Vis spectrum of the NR-β-CD@AuNPs (a) had two absorption bands at 520 nm and 450 nm, which correspond to the two states of NR. There were two new absorption bands appearing at 583 nm and 349 nm for the NO2-NR-β-CD@AuNPs. The color was also different when the NR-β-CD@AuNPs reacted with NO2−, as shown in Figure 7.

3.5. Selectivity

A 100-fold concentration of the other common ions were selected as competing ions in order to demonstrate the selectivity of this sensor, including Cl−, CO32−, HCO3−, F−, SO42−, H2PO4−, HPO42−, and NO3−. Meanwhile, [NO2−] of 0.35 μg·mL−1 was measured as the control group. As shown in Figure 8, the fluorescence quenching only occurred at 623 nm in the presence of NO2−, even though it contained other ions. These results emphasized the high selectivity of the fluorescence sensor for the trace detection of NO2−.

3.6. Application of NO2− Detection in Real Samples

The sensor was used to detect NO2− in the waters of a local river or pond to determine the realistic efficiency of an NR−β−CD@AuNP sensor. Recovery experiments were carried out on samples by adding nitrite ion standards [52]. The data are listed in Table 1, and the method has a recovery of 98.6−102.5% with a relative standard deviation (RSD) of less than 3%. The result indicated that the sensor was reliable for detecting NO2− in outdoor waters. It is confirmed that the NR−β−CD@AuNPs could be available for the detection of NO2− in real samples.

4. Conclusions

A fluorescence sensor was fabricated by modifying β−CD@AuNPs with NR for the trace detection of NO2−. The optional condition for the sensor was an acidic aqueous solution, and the detection limit was as low as 4.25 × 10−3 μg·mL−1. This sensor can selectively recognize NO2− through a visual color change from light purple or pink to light blue when the [NO2−] concentration is 0.30 μg·mL−1. When [NO2−] exceeded 0.9 μg·mL−1, the rate of fluorescence quenching reached 100%, and the color changed. The sensor was applied to the detection of NO2− in local waters with a low detection limit, wide linear concentration range, good reproducibility, and anti−interference ability.

Supplementary Materials

The following are available online at https://www.mdpi.com/1424-8220/18/3/681/s1. Figure S1: (A) UV-Vis spectrum of AuNPs; (B) TEM image of AuNPs, Figure S2: (A) Emission spectra of NR (a) NR-β-CD@AuNPs (b) and NR-β-CD(c); (B) TEM images of NO2-NR-β-CD., Figure S3: The regression equation in a weakly alkaline (A) and an acidic medium (B)., Figure S4: (A) Emission spectra of NR in the presence of different [NO2−], including 0, 0.10, 0.20, 0.30, 0.40, 0.50 and 0.60 μg∙mL−1. (B) Emission spectra of NR-β-CD in the presence of different [NO2−], including 0, 0.20, 0.40, 0.60, 0.80, 1.00, 1.20, 1.40, and 1.6 μg∙mL−1. Table S1: Comparison of the fabricated sensor with other reported sensors for nitrite ions.

Acknowledgments

This work was supported by the Projects of Wenzhou Science and Technology Bureau (S20150012) and (W20170006), the Science Foundation of Zhejiang Province (LY13B040002), and the National Natural Science Foundation of China (No. 31300819).

Author Contributions

Weilu Zhang and Lizhu Yang conceived and designed the experiments. Xiaoyang Du performed the experiments and analyzed the data. Xiaoxia Zhang contributed the reagents and materials. Chunlai Jiang validated the experiments. Weilu Zhang and Xiaoyang Du wrote the paper.

Conflicts of Interest

The authors declare no conflict of interest.

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Scheme 1. Schematic representation of the fabrication of the NR-β-CD@AuNP sensor and nitrite detection.
Scheme 1. Schematic representation of the fabrication of the NR-β-CD@AuNP sensor and nitrite detection.
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Figure 1. (A) UV-Vis spectra of the β-CD@AuNPs (a) and AuNPs (b); (B) FT-IR spectra of the β-CD@AuNPs (a) and SH-β-CD (b).
Figure 1. (A) UV-Vis spectra of the β-CD@AuNPs (a) and AuNPs (b); (B) FT-IR spectra of the β-CD@AuNPs (a) and SH-β-CD (b).
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Figure 2. TEM images and energy dispersive spectrometry (EDS) element mappings of the β-CD@AuNPs; the red and green colors correspond to elemental Au and S, respectively.
Figure 2. TEM images and energy dispersive spectrometry (EDS) element mappings of the β-CD@AuNPs; the red and green colors correspond to elemental Au and S, respectively.
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Figure 3. (A) Fluorescence spectra of the NR-β-CD@AuNPs when the volume of β-CD@AuNPs was 1, 2, 3, 4, 5, 6, 7, and 8 mL. (B) Plots of the NR-β-CD@AuNPs fluorescence intensities versus the volume of the β-CD@AuNPs with error bars. Inserted image: TEM image of the NR-β-CD@AuNPs.
Figure 3. (A) Fluorescence spectra of the NR-β-CD@AuNPs when the volume of β-CD@AuNPs was 1, 2, 3, 4, 5, 6, 7, and 8 mL. (B) Plots of the NR-β-CD@AuNPs fluorescence intensities versus the volume of the β-CD@AuNPs with error bars. Inserted image: TEM image of the NR-β-CD@AuNPs.
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Figure 4. (A) Excitation spectra of the NR-β-CD@AuNPs at pH values of 9, 7, and 5; (B) Emission spectra of the NR-β-CD@AuNPs at pH values of 9, 7, and 5; (C) Fluorescence intensity of the NR-β-CD@AuNPs (a) and the NR-β-CD@AuNPs in the presence of NO2− (100 μg·L−1) (b); Inserted image: TEM image of the NR-β-CD@AuNPs at a pH value of 5.
Figure 4. (A) Excitation spectra of the NR-β-CD@AuNPs at pH values of 9, 7, and 5; (B) Emission spectra of the NR-β-CD@AuNPs at pH values of 9, 7, and 5; (C) Fluorescence intensity of the NR-β-CD@AuNPs (a) and the NR-β-CD@AuNPs in the presence of NO2− (100 μg·L−1) (b); Inserted image: TEM image of the NR-β-CD@AuNPs at a pH value of 5.
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Figure 5. (A) Emission spectra of the NR-β-CD@AuNPs in the presence of different [NO2−] concentrations, including 0, 0.05, 0.10, 0.15, 0.20, 0.25, 0.30, 0.35, 0.40, 0.45, 0.50, 0.60, 0.70, 0.80, and 0.90 μg·mL−1 under a weakly alkaline medium; (B) Emission spectra of the NR-β-CD@AuNPs in the presence of different [NO2−] concentrations including 0, 0.05, 0.10, 0.15, 0.20, 0.25, 0.30, 0.35, 0.40, 0.45, 0.50, 0.60, 0.70, 0.80, and 0.85 μg·mL−1 under an acid medium.
Figure 5. (A) Emission spectra of the NR-β-CD@AuNPs in the presence of different [NO2−] concentrations, including 0, 0.05, 0.10, 0.15, 0.20, 0.25, 0.30, 0.35, 0.40, 0.45, 0.50, 0.60, 0.70, 0.80, and 0.90 μg·mL−1 under a weakly alkaline medium; (B) Emission spectra of the NR-β-CD@AuNPs in the presence of different [NO2−] concentrations including 0, 0.05, 0.10, 0.15, 0.20, 0.25, 0.30, 0.35, 0.40, 0.45, 0.50, 0.60, 0.70, 0.80, and 0.85 μg·mL−1 under an acid medium.
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Figure 6. Photograph of the NR-β-CD@AuNPs in the presence of different [NO2−] concentrations including 0, 0.05, 0.10, 0.20, 0.30, 0.40, 0.50, 0.60, 0.70, 0.80, 0.90, and 1.00 μg·mL−1; A: 0 μg·mL−1 of [NO2−] and competing ions; and B: 1.00 μg·mL−1 of [NO2−] and competing ions.
Figure 6. Photograph of the NR-β-CD@AuNPs in the presence of different [NO2−] concentrations including 0, 0.05, 0.10, 0.20, 0.30, 0.40, 0.50, 0.60, 0.70, 0.80, 0.90, and 1.00 μg·mL−1; A: 0 μg·mL−1 of [NO2−] and competing ions; and B: 1.00 μg·mL−1 of [NO2−] and competing ions.
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Figure 7. UV-Vis spectra of the NR-β-CD@AuNPs (a) and NO2-NR-β-CD@AuNPs (b).
Figure 7. UV-Vis spectra of the NR-β-CD@AuNPs (a) and NO2-NR-β-CD@AuNPs (b).
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Figure 8. (A) Fluorescence spectra of the (a) NR-β-CD@AuNPs; (b) NR-β-CD@AuNPs and competing ions (Cl−, CO32−, HCO3−, F−, SO42−, H2PO4−, HPO42− and NO3−); (c) NR-β-CD@AuNPs and NO2−; and (d) NR-β-CD@AuNPs, NO2− and competing ions. (B) Fluorescence intensity of the NR-β-CD@AuNPs and 1: blank, 2: Cl−, 3: CO32−, 4: HCO3−, 5: F−, 6: SO42−, 7: H2PO4−, 8: HPO42−, 9: NO3−, 10: NO2−, 11: NO2− and competing ions.
Figure 8. (A) Fluorescence spectra of the (a) NR-β-CD@AuNPs; (b) NR-β-CD@AuNPs and competing ions (Cl−, CO32−, HCO3−, F−, SO42−, H2PO4−, HPO42− and NO3−); (c) NR-β-CD@AuNPs and NO2−; and (d) NR-β-CD@AuNPs, NO2− and competing ions. (B) Fluorescence intensity of the NR-β-CD@AuNPs and 1: blank, 2: Cl−, 3: CO32−, 4: HCO3−, 5: F−, 6: SO42−, 7: H2PO4−, 8: HPO42−, 9: NO3−, 10: NO2−, 11: NO2− and competing ions.
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Table
Table 1. Results of the detection of nitrite ions in river (1) and pond (2) water (n = 6).
Table 1. Results of the detection of nitrite ions in river (1) and pond (2) water (n = 6).
SamplesContent (NO2−, μg·mL−1)Added (NO2−, μg·mL−1)Found (NO2−, μg·mL−1)Recovery (%)RSD (%)
10.23±0.010.100.33±0.01101.00±1.51.20±0.5
20.32±0.020.100.42±0.0199.80±1.22.10±0.7

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MDPI and ACS Style

Du, X.; Zhang, X.; Jiang, C.; Zhang, W.; Yang, L. The Trace Detection of Nitrite Ions Using Neutral Red Functionalized SH-β-Cyclodextrin @Au Nanoparticles. Sensors 2018, 18, 681. https://doi.org/10.3390/s18030681

AMA Style

Du X, Zhang X, Jiang C, Zhang W, Yang L. The Trace Detection of Nitrite Ions Using Neutral Red Functionalized SH-β-Cyclodextrin @Au Nanoparticles. Sensors. 2018; 18(3):681. https://doi.org/10.3390/s18030681

Chicago/Turabian Style

Du, Xiaoyang, Xiaoxia Zhang, Chunlai Jiang, Weilu Zhang, and Lizhu Yang. 2018. "The Trace Detection of Nitrite Ions Using Neutral Red Functionalized SH-β-Cyclodextrin @Au Nanoparticles" Sensors 18, no. 3: 681. https://doi.org/10.3390/s18030681

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