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Preparation of a Novel Clay/Dye Composite and its Application in Contaminant Detection

Published online by Cambridge University Press:  01 January 2024

Limei Wu ,
Xuyuan Bao ,
Haoyu Zhong ,
Yuwei Pan ,
Guocheng Lv  and
Libing Liao
Limei Wu
Affiliation:
School of Materials Science and Engineering, Shenyang Jianzhu University, Shenyang 110168, China
Xuyuan Bao
Affiliation:
The Beijing Municipal Key Laboratory of New Energy Materials and Technologies, School of Materials Sciences and Engineering, University of Science and Technology Beijing, Beijing 100083, China
Haoyu Zhong
Affiliation:
School of Materials Science and Engineering, Shenyang Jianzhu University, Shenyang 110168, China
Yuwei Pan
Affiliation:
School of Materials Science and Engineering, Shenyang Jianzhu University, Shenyang 110168, China
Guocheng Lv*
Affiliation:
Beijing Key Laboratory of Materials Utilization of Nonmetallic Minerals and Solid Wastes, National Laboratory of Mineral Materials, School of Materials Science and Technology, China University of Geosciences, Beijing 100083, China
Libing Liao
Affiliation:
Beijing Key Laboratory of Materials Utilization of Nonmetallic Minerals and Solid Wastes, National Laboratory of Mineral Materials, School of Materials Science and Technology, China University of Geosciences, Beijing 100083, China
*
*E-mail address of corresponding author: [email protected]
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Abstract

Although fluorescence detection is a sensitive method in the field of pollutant analysis, its application is restricted due to the fluorescence shown by organic material being quenched after aggregation and to low photo-thermal stability. To address these issues, a novel mineral/dye composite material was prepared by intercalating a fluorescence molecule, Rhodamine (R6G), into the interlayer space of montmorillonite (Mnt). This composite material greatly enhanced the light stability and efficiency of R6G. After enhancement, the fluorescence lifetime of R6G-Mnt was eight times longer than originally and the luminous intensity was 20 times greater. Chromium at the mmol/L (mM) level can be detected by the naked eye when its enhanced fluorescent property is fabricated into a solid test paper, even though a fluorescence spectrophotometer should be used for detection at the 0.01 μmol/L level in the sensing range 0.01 μmol/L to 100 mmol/L. These results can provide new avenues as well as a theoretical and experimental foundation for the development of novel supramolecular luminescent material.

Keywords

DetectionFluorescence quenchingInorganic/organic compositeLight-emitting efficiency
Type
Original Paper
Information
Clays and Clay Minerals , Volume 67 , Issue 3 , June 2019 , pp. 244 - 251
Copyright
Copyright © Clay Minerals Society 2019

Introduction

Fluorescent materials and their derivatives are used widely, especially in functional materials, such as: pH test strips, formaldehyde test kits, etc., as well as in biological and medical fields (Haugland Reference Haugland1994). The broad applications of organic fluorescent materials in diverse areas are due to their flexible structures (Skaff et al. Reference Skaff, Sill and Emrick2004; Zhang et al. Reference Zhang, Wang, Li, Ji, Zhang and Yang2005). Several dye compounds can be used in the luminous field; their applications, however, are limited by multiple drawbacks (e.g. concentration quenching and low-light thermal stability in the solid state) (Lee et al. Reference Lee, Sundar, Heine, Bawendi and Jensen2000; Zhang et al. Reference Zhang, Cui, Wang, Zhang, Ji, Lu, Yang and Gao2003).

Chromium (Cr) compounds are used widely in various sectors of industry (Mondal Reference Mondal2009; Olmez Reference Olmez2009). Cr is a major industrial pollutant and its concentration in the environment keeps increasing due to its extensive use in leather tanning, stainless-steel production, and electroplating (Lalvani et al. Reference Lalvani, Wiltowski, Hubner, Weston and Mandich1998; Kantar et al. Reference Kantar, Cetin and Demiray2008). A rapid and efficient way to detect Cr(VI) is, therefore, crucial in the development of water contaminant treatment. Detection of Cr(VI) is most commonly performed by using atomic absorption spectroscopy, inductively coupled plasma mass spectrometry, and electrochemical methods (Sperling et al. Reference Sperling, Xu and Welz1992; Powell et al. Reference Powell, Boomer and Wiederin1995; Zheng et al. Reference Zheng, Xie, Qu, Li, Du, Jing and Sun2013). Many of these methods are sensitive and accurate, but they are also costly and require sophisticated instrumentation. A clear, unmet need exists for sensitive, specific, and selective detection and quantification of Cr(VI). Fluorescence spectroscopy is used increasingly, due to its sensitivity compared to other techniques (Nolan & Lippard Reference Nolan and Lippard2008) and, coupled with organic and inorganic semiconducting luminescent materials, have shown great promise (George et al. Reference George, Rao and Jain2014).

Fluorescent chemical sensing materials and their applications have been a focus for some time in interdisciplinary research (Zheng et al. Reference Zheng, Orbulescu, Ji, Repoulos, Pham and Leblanc2003; Shi et al. Reference Shi, Wang, Ji, Gao and Wang2005; Austin et al. Reference Austin, Perry, Richter and Schroeder2018). Fluorescent chemical sensing materials use probe molecules to form chemical bonds or supramolecular interactions with target molecules, quenching or enhancing the fluorescence of the molecules. Hence, easy, highly sensitive detection of target molecules or ions is achieved (Patra & Mishra Reference Patra and Mishra2002). For instance, the detection limit of phenol can be as low as 1 μM (Sergeyeva et al. Reference Sergeyeva, Chelyadina, Gorbach, Brovko, Piletska, Piletsky, Sergeeva and Elskaya2014). All detection of contaminants should be carried out under the same conditions, however (Goswami et al. Reference Goswami, Paul and Manna2013; Bao et al. Reference Bao, Shi, Nie, Zhou, Wang, Zhang, Liao and Pang2014; Lee et al. Reference Lee, Lim, Suh, Song and Kim2014); organic solvents used in the process also cause environmental problems (Ego et al. Reference Ego, Marsitzky, Becker, Zhang, Grimsdale, Müllen, Mackenzie, Silva and Friend2003).

The use of weak interaction forces (hydrogen bond, hydrophobicity, Van der Waals force, п-п, and static electricity) between the inorganic molecules (host) and organic probe molecules (guest) to formulate inorganic-organic hybrid fluorescent chemical materials has been studied previously (see, for example, Karataş et al. Reference Karataş, Tekin and Çelik2017). The process of supramolecular formulation is simple and widely applicable (Gao et al. Reference Gao, Ye, Cui and Zhang2012). Layered, two-dimensional nano-materials have large specific surface areas and homogeneous surface properties, and tend to form multi-layer structures in supramolecular formulations because of their large cation exchange capacity (CEC), and, to a certain extent, pseudo-agglomeration of probe molecules. These advantages facilitate layered two-dimensional nano-materials as a host prior to the formulation of inorganic-organic fluorescent materials. Clay minerals provide distinct nanometer-scaled layers and interlayers for engineering as selective and active adsorbents and catalysts (Zhou et al. Reference Zhou, Zhao, Wang, Chen and He2016). As a vital clay mineral, montmorillonite (Mnt) is a 2:1 phyllosilicate mineral that consists of layered silicon tetrahedral and aluminum octahedral sheets with negatively charged layers compensated by cations, such as Na+ and Ca2+ (Whitney & Evans Reference Whitney and Evans2010; Wu et al. Reference Wu, Liao, Lv, Qin and Li2014a). Mnt has a large CEC; the cations can thus be replaced by other inorganic or organic cations. This is an effective way to construct ordered inorganic-organic and inorganic-inorganic assemblies with unique microstructures and properties. The Mnts have attractive properties, including large specific surface area, swellability, adsorption capacity, and cation exchange capacity. These features facilitate the formulation of fluorescent molecules in Mnt interlayer spaces and, thereby, provide good potential for the development of fluorescent sensor materials for the detection of trace contaminants. The electrostatic charge on the layers plays a leading role in the attraction between clay minerals and organic material (Čeklovský et al. Reference Čeklovský, Czímerová, Lang and Bujdák2009; An et al. Reference An, Zhou, Zhuang, Tong and Yu2015; Zhou et al. Reference Zhou, Zhou, Wu, Jiang, Xia, Li and Yu2019).

The objective of the current study was to use clay/organic intercalation composites as novel fluorescent materials, fabricated by the controlled assembly of fluorescent molecules into the Mnt interlayer, to achieve sensitive detection of trace Cr(VI) in water (Fig. 1) These composites have greater sensitivity than the 7-amino-4-methylcoumarin/montmorillonite composite fabricated by Wei et al. (Reference Wei, Mei, Li, Liu, Lv, Weng, Liao, Li and Lu2018). The hypothesis was that the outcomes would add more fundamental understanding of the assembly mechanisms for guest–host interactions and would provide novel ideas for future development and applications of sensing materials.

Fig. 1. Schematic view of the preparation of R6G -Mnt and the detection of Cr(VI)

Experimental and Methods

Montmorillonite (SWy-2) was obtained from the Source Clays Repository of The Clay Minerals Society. Details of the Mnt were given by Wu et al. (Reference Wu, Liao, Lv, Qin and Li2014a).

Rhodamine 6G (R6G) is a catechol compound (Fig. 2) which possesses a large degree of conjugation. It is a red or yellowish brown powder, soluble in water. R6G aqueous solution is scarlet in color, with a green fluorescence. The R6G molecule is 12.5 Å wide and 7.14 Å high. The initial concentrations of R6G varied from 0.1 to 10.5 mM for the adsorption isotherm study. The R6G-Mnt was prepared by the method of Lv et al. (Reference Lv, Liu, Liu, Liao, Wu, Mei, Li and Pan2018).

Fig. 2 The structure of R6G

A UV-Vis spectrophotometer (SPECORD 50 plus, made by Analytik Jena AG, Beijing, China) operated at a wavelength of 527 nm was used to analyze the equilibrium R6G concentrations. Powder XRD analyses were performed using a Rigaku D/max-IIIa diffractometer (Tokyo, Japan) with Ni-filtered CuKα radiation at 30 kV and 20 mA. The data for orientated samples were collected over the range (3°–70°2θ) with a scanning step of 0.01°2θ and a scanning speed of 2°2θ/min. A fluorescence spectrophotometer (HITACHI, F4600, Beijing, China) with a photomultiplier tube operating at 400 V and an excitation source with a 150 W xenon lamp was used to measure the photoluminescence excitation (PLE) and emission (PL) spectra. The lifetimes were recorded on a spectro-fluorometer (HORIBA, JOBIN YVON FL3-21, Edinburgh, UK) with a 210 nm pulse laser radiation (nano-LED) as the excitation source.

Molecular simulation was carried out under the module CASTEP of Materials Studio 6.0 software to study the configuration of the uptake of R6G by Mnt (Wu et al. Reference Wu, Liao, Lv, Qin and Li2014a). The unit-cell parameters were a = 15.540 Å, b = 17.940 Å, c =12.56 Å, α = γ = 90°, and β = 99°. A series of (3×2×1) supercells was built with the layer spacing set at 15.08 and 20.45 Å for Mnt and R6G-Mnt, respectively.

Results and Discussion

Preparation and Characterization of R6G-Mnt Luminescent Composites

Rhodamine (R6G) has a pKa value of 7.5 (Khurana & Santiago Reference Khurana and Santiago2009); as the equilibrium solution pH value was ~3–5, most of the R6G existed as a monovalent cation (Zhang et al. Reference Zhang, Xu, Su, Shen, Xie and Tian2011; Lee et al. Reference Lee, Jang and Polyakov2015). The amount of R6G adsorbed by Mnt increased as the concentration of the solution increased (Fig. 3). The adsorption capacity increased sharply when the concentration of R6G was ~0.1–5 mM, and then showed a slow increase when the concentration of R6G was >5 mM. When the concentration was 8 mM, the adsorption reached a balance point and the amount of RG6 intercalated into Mnt showed a maximum value of 0.8 mmol/g. This indicates that the amount of R6G intercalated into Mnt is related to the amount of R6G adsorbed by Mnt . The intercalation quantity affects the distribution of R6G in the interlayer space of Mnt (Wu et al. Reference Wu, Liao, Lv, Qin and Li2014a).

Fig. 3. Adsorption curves of rhodamine by montmorillonite (R6G-Mnt)

The degree of intercalation by R6G is reflected by the d 001 value of R6G-Mnt as determined by XRD. The interlayer spacing of Mnt was related to the initial concentration of R6G solution. R6G replaced Na as the interlayer cation, and thus increased the d 001 spacing (Fig. 4) from an initial value of 1.29 nm to 1.58 nm when the initial concentration of R6G was 0.1 mM, and reached a maximum value (2.05 nm) when the concentration of R6G was 3 mM. The trend for the basal spacing (d 001) was the same as that for the interlayer space. The different properties of R6G-Mnt were due to the different incorporation and arrangement of intercalation (Wu et al. Reference Wu, Yang, Mei, Qin, Liao and Lv2014b). The results confirm that the hydrophobic force among alkyl chains of organic cations is the driving force for their intercalation (Dultz et al. Reference Dultz, Riebe and Bunnenberg2005; Klebow & Meleshyn Reference Klebow and Meleshyn2012; Yu et al. Reference Yu, Zhu, Tong, Wang, Wu and Zhou2017).

Fig. 4. X-ray diffraction patterns of R6G-Mnt at various concentrations of R6G

The intercalation of R6G into Mnt not only affected the interlayer spacing but also the arrangement of interlayer R6G and its interaction force with the Mnt layer. Pure R6G has an extremely low luminous intensity because of the concentration quenching effect; after being intercalated into the interlayer of Mnt, the luminous intensity was notably improved. In the emission spectrum of R6G at different amounts of intercalation (Fig. 5), when the initial concentration of R6G solution was 0.5 mM, R6G-Mnt had its greatest spectral intensity. At other concentrations, spectral intensities were lower, indicating that too much or too little intercalation of R6G reduced the luminous intensity of R6G-Mnt.

Fig. 5 Fluorescence spectra of the R6G and R6G-Mnt

The lifetime of a luminous material is an indicator of its stability. The lifetime of R6G is only 4.1 ns (Magde et al. Reference Magde, Wong and Seybold2002); this improves significantly after intercalation into Mnt (Fig. 6). At an initial concentration of 0.5 mM, R6G had the longest lifetime (31.12 ns), which is almost eight times greater than that of the original and better than other assembly techniques (Yan et al. Reference Yan, Lu, Ma, Qin, Wei, Evans and Duan2011a; Yan et al. Reference Yan, Lu, Ma, Wei, Evans and Duan2011b). The interactions between the Mnt layer and the interlayer R6G, which had a supramolecular structure, had a significant effect on the lifetime and aging resistance of R6G. The results of this study may solve the problems of low thermal stability and short lifetime in the application of organic luminous molecular devices (Wu et al. Reference Wu, Lv, Liao and Qin2015a, Reference Wu, Lv, Liu, Li, Liao and Pan2015b).

Fig. 6. Fluorescence decay curves of R6G-Mnt

Cr(VI) Detection in Aqueous Phase by R6G-Mnt

Good fluorescence makes R6G-Mnt a suitable fluorescent detector of contaminants. The addition of Cr(VI) triggered an apparent quenching of the R6G-Mnt peak (Fig. 7). When the concentration of Cr(VI) was increased from 0 to 20 mM, a gradual reduction in the PL spectrum was observed. When the concentration of Cr(VI) was 20 mM, the PL spectrum was half what it was when the concentration was 0.0 mM. Reduction in Cr(VI) led to a regular increase in PL spectra in conjugates and the fluorescence intensity ratio (F/F0) varied linearly with the addition of Cr(VI) in the range 0.01–1.2 μM (R2 = 0.9892) (Fig. 7 inset). R6G has a lower detection limit than the 7-amino-4-methylcoumarin/montmorillonite composite (Wei et al. Reference Wei, Mei, Li, Liu, Lv, Weng, Liao, Li and Lu2018). For this proposed method, the limit of detection (LOD) was 10.08 ± 0.11 nM, which was calculated using 3σ/k (where σ is the standard deviation for six replicating detections of blank solutions and k is the slope of the calibration curve) (Wu & Yan Reference Wu and Yan2010; Lv et al. Reference Lv, Liu, Liu, Liao, Wu, Mei, Li and Pan2018) and was better than that of other related single-intensity-based PL sensors (Xu et al. Reference Xu, Miao, Fang and Zhong2011; Gui et al. Reference Gui, An, Su, Shen, Chen and Wang2012; Irannajad & Haghighi Reference Irannajad and Haghighi2017).

Fig. 7. Fluorescence spectra of R6G-Mnt in an aqueous buffer in the presence of various concentrations of chromium. Inset: fluorescence intensity ratio (F/F 0) changes at 527 nm

To compare the detecting efficiency of R6G-Mnt for several typical cationic contaminants, R6G-Mnt was made into round disks with a diameter of 1 cm and placed in Cr(VI), Fe(III), and Cu(II) solutions with various concentrations (Table 1). The fluorescence quenching of R6G-Mnt increased with increase in Cr(VI) concentration. When Cr(VI) solution (0–~100 mM) was added to an R6G-Mnt wafer, the increase in fluorescence quenching could be distinguished by the naked eye. These results suggest that Cr(VI) induced PL quenching of conjugates with high selectivity. The fluorescence intensity in images of R6G-Mnt following addition of Cr(VI) under fluorescent light decreased as the chromium concentration increased (Fig. 8). Next, R6G-Mnt was made into a test paper to examine luminescence when various concentrations of Cr(VI) solution interacted with R6G-Mnt. The examination showed quick and accurate detection of Cr(VI) by R6G.

Table 1 Image of R6G-Mnt in aqueous buffer in the presence of various concentrations of Cr6+, Fe3+, and Cu2+

Fig. 8. Images of R6G-Mnt with various concentrations of chromium under ultraviolet light. The contrast between the letters and the background becomes stronger as the chromium concentration increases

Mechanism of Detection of Cr(VI) by R6G-Mnt

The interlayer spacing of Mnt plays a crucial role in the system’s structure and interaction forces (Tong et al. Reference Tong, Djurisić, Xie, Ng, Cheung, Chan, Leung, Lin and Gwo2006; Krauss et al. Reference Krauss, Barrena, Lohmuller, Spatz and Dosch2011; Wang et al. Reference Wang, Liu and Pan2011). Mnt with the interlayer R6G arranged in a parallel fashion has a smaller interlayer spacing than Mnt with R6G tilted or vertical. (Fig. 9). Taking into account the amount of intercalated R6G and the change in the Mnt interlayer spacing, the orientation distances of –N+ groups to the Mnt layer were calculated by molecular simulation for various intercalation amounts and interlayer distance. At concentrations of 0.5 mM and 3 mM, the numbers of intercalated molecules in Mnt were 2 and 4, respectively, and the corresponding arrangements of R6G in the Mnt space were tilted monolayer and tilted bilayer, respectively, while the distances of –N+ groups from the Mnt layer were 1.446 and 1.887 Å, respectively. Based on these results, the luminescence of R6G-Mnt was related to the amount of R6G intercalated into Mnt and also to the arrangement of R6G in Mnt space. Pure R6G showed poor luminescence because of the concentration quenching effect. Similarly, when the amount of R6G intercalated was >0.4 mmol/g, the intermolecular force could increase and concentration quenching also occurred (Montalti et al. Reference Montalti, Prodi, Zaccheroni and Falini2002). A large concentration (>0.3 mmol/L) of R6G caused a stronger interaction force between molecules, leading to quenching. The molecule-end amino twirling aggravated internal conversion, broke the rigid plane of oxygen in the heteroanthracine parent ring, and consequently reduced the production of fluorescence quanta. For relatively small amounts (<0.2 mmol/g) intercalated, R6G molecules were restricted and distributed evenly in Mnt space, which led to a separation of R6G molecules from each other, reduced the intermolecular force, and prevented concentration quenching. When the intercalation of R6G into Mnt was 0.08 mmol/g and R6G was distributed uniformly in the interlayer, the luminescence of R6G -Mnt composite was at a maximum.

Fig. 9 Molecular dynamics simulation of intercalation for various arrangements of R6G in Mnt. For all species, C = gray, N = blue, H = white, O = red, Si = yellow, Al = pink, and Mg = green

Conclusions

In summary, a novel supramolecular structure was constructed by intercalating R6G into Mnt. The R6G-Mnt composite exhibited significantly improved luminescence properties, including strong luminescence intensity and long lifetime, which indicates that R6G-Mnt may have potential applications in display and lighting devices. The introduction of Cr(VI) caused quenching of R6G-Mnt fluorescence, resulting in a high sensitivity to, and low detection limit of, Cr(VI). The outcome of this study provides more fundamentals for comprehension of the mechanism of guest–host interactions in the assembly, future development, and application of sensing materials.

Acknowledgments

This research was funded jointly funded by the China Postdoctoral Science Foundation funded project (2018M631818) and the Doctoral Startup Foundation of Liaoning (20170520315).

Conflict of Interest

There are no conflicts of interest to declare.

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Figure 0

Fig. 1. Schematic view of the preparation of R6G -Mnt and the detection of Cr(VI)

Figure 1

Fig. 2 The structure of R6G

Figure 2

Fig. 3. Adsorption curves of rhodamine by montmorillonite (R6G-Mnt)

Figure 3

Fig. 4. X-ray diffraction patterns of R6G-Mnt at various concentrations of R6G

Figure 4

Fig. 5 Fluorescence spectra of the R6G and R6G-Mnt

Figure 5

Fig. 6. Fluorescence decay curves of R6G-Mnt

Figure 6

Fig. 7. Fluorescence spectra of R6G-Mnt in an aqueous buffer in the presence of various concentrations of chromium. Inset: fluorescence intensity ratio (F/F0) changes at 527 nm

Figure 7

Table 1 Image of R6G-Mnt in aqueous buffer in the presence of various concentrations of Cr6+, Fe3+, and Cu2+

Figure 8

Fig. 8. Images of R6G-Mnt with various concentrations of chromium under ultraviolet light. The contrast between the letters and the background becomes stronger as the chromium concentration increases

Figure 9

Fig. 9 Molecular dynamics simulation of intercalation for various arrangements of R6G in Mnt. For all species, C = gray, N = blue, H = white, O = red, Si = yellow, Al = pink, and Mg = green