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Article

Cholesteric Liquid Crystal Photonic Hydrogel Films Immobilized with Urease Used for the Detection of Hg2+

Key Laboratory of Colloid and Interface Chemistry, Shandong University, Ministry of Education, Jinan 250100, China
*
Author to whom correspondence should be addressed.
These authors contributed equally to this work.
Submission received: 15 February 2022 / Revised: 2 April 2022 / Accepted: 6 April 2022 / Published: 8 April 2022
(This article belongs to the Special Issue Feature Papers on Luminescent Sensing)

Abstract

:
Mercury ion is one of the most widespread heavy metal contaminants which can accumulate in the body through multiple channels, posing a detrimental impact on human health. We demonstrate a simple and low-cost method for the detection of Hg2+ assisted by a cholesteric liquid crystal photonic hydrogel (polyacrylic acid (PAA)) film with immobilized urease (CLC-PAAurease film). In the absence of Hg2+, a significant change in color and an obvious red shift in the reflected light wavelength of the prepared film were observed, since urease can hydrolyze urea to produce NH3, resulting in an increasing pH value of the microenvironment of CLC-PAAurease film. Hg2+ can inhibit the activity of urease so that the color change of the film is not obvious, corresponding to a relatively small variation of the reflected light wavelength. Therefore, Hg2+ can be quantitatively detected by measuring the displacement of the reflected light wavelength of the film. The detection limit of Hg2+ is about 10 nM. This approach has a good application prospect in the monitoring of heavy metal ions in environmental water resources.

1. Introduction

With the development of modern industry, heavy metal ion pollution has become a great danger to the environment and the human body [1]. Hg2+ is a highly toxic heavy metal ion. It accumulates in large quantities in rivers and aquatic organisms and enters the human body through the food chain and other channels [2,3]. Due to its non-biodegradable and accumulative nature, Hg2+ cannot be excreted from the body. It can cause varying degrees of damage to the human respiratory, digestive and nervous systems, even in very small amounts [4,5]. Hg2+ in the environment combines with various ligands to form complexes and is converted to methylmercury and dimethylmercury by the action of microorganisms, which is known as the biomethylation of mercury [6,7,8]. Because methylmercury is readily soluble in lipids and the carbon–mercury bonds in its molecular structure are not readily broken down, it is readily absorbed by the body, excreted slowly and has a higher toxicity profile. Therefore, the detection of Hg2+ has attracted much attention [9].
A variety of Hg2+ detection methods have been established such as atomic absorption spectrometry [10,11,12], inductively coupled plasma mass spectrometry (ICP-MS) [13,14,15], electrochemical methods [16,17,18] and fluorescence spectrometry [19,20,21]. Although these assays of Hg2+ have high sensitivity, they usually require large, expensive instruments, specialized technicians and time-consuming operations [22]. In addition, some existing Hg2+ detection methods even require molecular markers, which are not conducive to the rapid and continuous monitoring of Hg2+ in actual environments. Therefore, it is an urgent task to develop a new strategy to detect Hg2+ with some advantages such as low cost and simple operation.
The photonic crystal (PC) has broad application prospects in constructing the optical sensor, which can be attributed to its excellent optical properties [23,24,25]. The cholesteric liquid crystal (CLC) is a periodic arrangement of twisted layers of parallel, aligned rod-like molecules or nano-objects and has attracted much attention in the construction of sensors because of its special spiral structure and the easy preparation of the one-dimensional PC structure [26]. It is a liquid crystal with photonic bandgap properties and a strong spin, pronounced circular dichroism and selective reflection of light that can be seen very clearly with the naked eye as a change in color [27,28]. The molecules are arranged in parallel layers in the plane and the orientation of the molecules in the adjacent layers varies helically in the direction normal to the plane. The color reflected by the CLC photonic crystal is related to its pitch [29]. The pitch of the cholesteric phase liquid crystal can be regulated by simply changing the concentration of chiral molecules doped during the preparation process, and can be polymerized into stable films under UV illumination. The prepared solid film is easy to preserve and transport, making it very widely used [30,31].
The CLC PC films are mainly used to detect volatile organic compounds (VOC) based on the change in pitch size in the microstructure, resulting in the obvious color variation of the films on the macroscopic level [32,33]. Recently, a widely used stimulus-responsive CLC PC film was constructed by combining the responsive functional materials with CLC PC. The optical signal of the CLC PC sensor can be changed by different physical factors such as pressure, temperature and humidity [34,35,36]. In addition, biological or chemical reactions can be initiated in the CLC PC films to achieve the analysis and detection of specific targets [37,38,39,40].
Polyacrylic acid (PAA) hydrogel is a polymer material with an interpenetrating three-dimensional network structure. The molecular chain of PAA contains a large number of ionizable COOH groups and is therefore a pH-sensitive smart polymer. When the pH value of the solution is higher than the pKa of acrylic acid, COOH is dissociated, the free energy of the system is reduced, and the gel swells by absorption; when the pH is lower than the pKa of acrylic acid, due to the hydrogen bonding between COOH, in this case the conformation of the PAA molecular chain is curled compared with the high pH. Under this condition, the hydrophilicity of the PAA is relatively weaker and its hydrophobicity is relatively stronger. Therefore, the swelling degree of the gel is reduced [41,42] and it possesses obvious reversible shrinkage or expansion ability under pH variation [43].
In recent years, several groups have designed and prepared a series of responsive photonic gels based on the property that responsive gels produce strong volume expansion and contraction when stimulated by external conditions [44,45,46]. As such, photonic crystal hydrogels, the most prevalent of the gels, have become one of the research hotspots in the field of sensing technology. By introducing polymer hydrogels into arrays of crystallized colloidal microspheres (e.g., silica, polystyrene microspheres), hydrogel complexes with a controlled and ordered photonic band gap structure can be formed. Changes in the external environment can lead to expansion or contraction in the volume of the polymer hydrogel, which in turn leads to changes in the lattice spacing of the colloidal microsphere array, displacing the Bragg diffraction peak and leading to color changes in the photonic crystal hydrogel [47,48,49]. Photonic crystal gels have been used to detect mercury ions and other substances and have shown good response properties [50,51]. CLC with better optical properties is relatively simple to prepare, and more sensitive to color changes compared with other photonic crystals. Stumpel et al. [31] prepared a stimulus-responsive cholesteric liquid crystal-hydrogel polymer network (CLC-PAA) material by using the PAA hydrogel and the CLC PC structure. The color of CLC-PAA hydrogel film was changed, obviously caused by the increase or decrease in the CLC pitch through the swell or contract of the PAA hydrogel when the pH was changed.
Herein, a method for detecting Hg2+ is proposed by using a cholesteric liquid crystal photonic hydrogel film immobilized with urease (CLC-PAAurease film as a sensitive recognition element. As shown in Figure 1, urease can catalyze the hydrolysis of urea and produce NH3, leading to an elevated pH in the PAA hydrogel. The PAA hydrogel belongs to a class of pH-sensitive anionic hydrogels with abundant -COOH on its chain skeleton. The hydrogel has a higher swelling rate at a higher pH, causing an increase in the pitch of the photonic crystal, resulting in the red shift of its diffraction wavelength. In contrast, in the absence of Hg2+, the hydrolysis of urea by urease is blocked because the urease activity is inhibited. At the same time, the color of the CLC-PAA PC film changes slowly, and detection of the target Hg2+ can be realized based on the shift of the reflected light wavelength of the film.

2. Materials and Methods

2.1. Experimental Materials

2-(N-Morpholino) ethanesulfonic acid (MES) was purchased from Shanghai Acmec Biological Co., Ltd. (Shanghai, China). N-Hydroxysuccinimide (NHS), urea and urease (Jack Bean) were provided by Shanghai Yuanye Bio-Technology Co., Ltd. (Shanghai, China). 1-(3-Dimethylaminopropyl)-3-ethylcarbodiimine hydrochloride was purchased from Macklin Biochemical Co., Ltd. (Shanghai, China). 1,4-Bis-[4-(3-Acryloyloxypropyloxy) benzoyloxy]-2-methylbenzene (RM257) was provided by Bide Pharmatech Ltd. (Shanghai, China) (S)-4’-(2-Methylbutyl)-[1,1’-biphenyl]-4-carbonitrile (CB15) and acrylic acid (AA) were ordered from Sigma-Aldrich company (St. Louis, MO, USA). α-Hydroxyisobutyryl benzene (Irgacure 1173) was provided by Shanghai Darui Fine Chemical Co., Ltd. (Shanghai, China). Tripropanediol diacrylate (TPGDA) was purchased from Heowns Biochem Technologies LLC., Tianjin, China. Mercury ion standard solution (100 μg/mL) was purchased from Shanghai Acmec Biochemical Co., Ltd. (Shanghai, China). Trometamol (Tris) was purchased from Sangon Biotech Co., Ltd. (Shanghai, China). N, N-Dimethyl-N-octadecyl (3-aminopropyl)trimethoxysilyl chloride (DMOAP) was provided by Energy Chemical Co., Ltd. (Shandong, China). Potassium hydroxide (KOH) and acetone were purchased from Laiyang Kangde Chemicals Co., Ltd. (Shandong, China). Nitrogen was ordered from Jinan Deyang Special Gas Co., Ltd. (Shandong, China). Methanol and ethanol were purchased from Tianjin Fuyu Fine Chemical Co., Ltd. (Tianjin, China). All the chemicals were used without further purification.

2.2. Experimental Apparatus

Cary 5000 UV–Vis spectrophotometer (Agilent, Palo Alto, CA, USA) was used to characterize the reflectance spectra of CLC-PAA photonic crystal gel films with a resolution better than 0.048 nm. Tensor II FTIR (Bruker, Germany) was employed to characterize the successful cross-linking of urease in CLC-PAA photonic crystal gel films using potassium bromide pressed slices with a resolution better than 0.4 cm−1. JSEM-6700F scanning electron microscope (JEOL, Tokyo, Japan) was used to observe the changes in the cut surface morphology of CLC films before and after cross-linking with PAA. The prepared films were fixed to the silicon wafer using conductive adhesive and the surface of the composite film was sprayed with gold to enhance its electrical conductivity before testing. AG-2000A Tensile tester (SHMADZU, Tokyo, Japan) was utilized to test the tensile properties of CLC, PAA and CLC-PAA films.

2.3. Preparation of Hydrogel

The precursor of PAA hydrogel was composed of AA, TPGDA and Irgacure 1173, which should be kept in a dark place. The glass slides were cleaned with cleaning agent to remove the oil stain on the surface, then cleaned with a large amount of ultra pure water, methanol, and ethanol, respectively. Finally, the glass slides were dried with nitrogen in the oven at 110 °C for 1 h and were then kept in a desiccator. The cleaned glass slides were cut into square glasses which were used for the preparation of PAA hydrogel films.

2.4. Preparation of CLC Photonic Crystal Film

We obtained the color liquid crystals (CLC photonic crystal) by mixing chiral dopant (CB15) and RM257 in a certain proportion at 60 °C for 6 h. Then, a small amount of CLC photonic crystal was placed in the center of the glass slide, another slide was covered, and the two ends of the two slides were fixed by a long-tail clamp. Finally, we obtained the CLC photonic crystal films by UV polymerization through a portable ultraviolet (UV) lamp (365 nm) for 10 min.

2.5. Preparation of CLC-PAA Photonic Crystal Gel Film

The prepared CLC photonic crystal films were continuously cleaned and soaked in acetone to completely remove the chiral dopant (CB15). Then, the precursor of PAA hydrogel was immersed in the CLC photonic crystal films which removed the chiral dopant. The thickness of the film was controlled by the long tail clamp. Finally, we obtained the CLC-PAA photonic crystal film using the portable UV lamp for 10 min.

2.6. Preparation of CLC-PAAurease PC Film

The excess AA on the CLC-PAA photonic crystal film was removed using a large amount of water in order to activate the carboxyl group on the prepared films that were placed in EDC/NHS (0.2 M/0.2 M) MES buffer solution. Next, they were incubated with the urease in PBS buffer for 1 h at room temperature. Finally, we used a large amount of PBS buffer for flushing out the films, and they were dried naturally at room temperature to obtain the CLC-PAA photonic crystal gel film with immobilized urease (CLC-PAAurease PC film).

2.7. Detection of Hg2+

The CLC-PAAurease PC film was used to detect Hg2+. The different concentrations of Hg2+ solutions were dropped on the prepared films to inhibit the activity of urease. Then, we placed the rinsed off Hg2+ films in a urea solution (10 mM) for 10 min at room temperature. Then, the films that inhibited urease activity were reacted with urea for 10 min. Finally, we obtained the concentrations of Hg2+ through the wavelengths of the reflected light of these films by UV–vis spectra. To verify the selectivity of the CLC-PAAurease PC film, Hg2+ was replaced by Ca2+, Cu2+, Zn2+, Al3+ and Fe3+ with other conditions unchanged.

3. Results and Discussion

3.1. Subsection Structure Characterization of CLC-PAA PC Films

It is reported that PAA hydrogels possess a rapid pH response, good biocompatibility, and an interpenetrating network structure. The PAA hydrogels were cross-linked in the CLC PC films to enable the pH responsiveness of the materials. Firstly, we prepared the PAA hydrogel film and explored its properties. Figure 2 shows that the prepared PAA hydrogel film has an obvious swelling property in water. As we see in Figure 3a, the swelling ratio (φ) of the PAA film is a function of the amount of TPGDA (ζ). It was found that φ reaches a maximum when the value of ζ is 0.5 wt%. However, φ decreases at the ζ of more than 0.5 wt% due to the cross-linked structure. Therefore, the optimum condition of TPGDA for the preparation of the PAA hydrogel film was 0.5% which was selected to carry out the subsequent experiments. Figure 2b shows φ of the PAA hydrogel film (ζ = 0.5 wt%) at different pH. Apparently, within the pH range investigated, the values of φ increase as the pH increases (Figure 3b).
Subsequently, we prepared the CLC photonic crystal films with a flat surface (Figure 4a) and a thickness of about 26.69 μm (Figure 4b). Then, we processed the above films (the chiral dopant CB15 was removed and PAA was crosslinked) to prepare the CLC-PAA photonic crystal gel film. As can be seen from the UV-visible spectrum in Figure 4c, there is a significant red shift in the wavelength of the reflected light from the films after the removal of the chiral dopant CB15 and cross-linking of the PAA. In addition, the inset of Figure 4c shows photographic images of the extracted CLC PC CB15 solid film, the CLC PC film and the CLC-PAA PC film. They show blue, blue-green, and green colors, respectively, indicating that the AA/TPGDA was successfully penetrated and UV-cured in the CLC PC films.
Figure 5a,b separately show the SEM images of the cross-section surface of the CLC PC film before and after the infiltration and crosslinking of the AA/TPGDA (CLC-PAA PC hydrogel film), which displays a significant change in the pitch of the helix. In addition, with the participation of the PAA, the pitch of the PC film becomes larger and its serrated structure grows thicker after cross-linking the hydrogel, which are the characteristics of the structural properties of the PAA hydrogel. Therefore, the PAA hydrogels were successfully cross-linked into the CLC PC films.
Subsequently, we measured the tension–strain curves of the CLC, PAA and CLC-PAA films, which indicated that the mechanical properties of the CLC films were improved after the AA/TPGDA was cross-linked by the CLC films (Figure 6). It follows that the PAA hydrogel was introduced into the CLC film successfully. This remarkably improved the mechanical strength of the CLC film, which facilitates the reusability of the film in analytical assays.

3.2. PH Response of CLC-PAA PC Films

The pH response of the CLC-PAA PC films is shown in Figure 7. As expected, the color of the prepared films changed distinctly from green to orange-yellow when the experimental conditions were changed from pH = 4 to pH = 12. Furthermore, the wavelength of the reflected light increases as the pH increases, which shows an obvious redshift. This result indicates that the PAA hydrogels expand at a high pH and correspondingly increase the helix pitch of the CLC PC films. Thus, local pH changes can be employed in the CLC-PAA films for sensor construction, which can be used to detect heavy metal ions without sophisticated instruments.

3.3. Crosslinking of Urease on the CLC-PAA PC Films

We studied the structure of the CLC-PAA PC films and the urease immobilization using Fourier transform infrared (FTIR) spectroscopy. The FTIR spectrum of the CLC solid films (Figure 8a) shows -CH2-, -C=O, -Ar-O-, and -Ar- stretching bands at 2839, 1720, 1257, and 840 cm−1, respectively. These peaks may result from RM257. The FTIR spectrum of the CLC-PAA hydrogel films (Figure 8b) shows the same peaks as the CLC solid film with new peaks derived from the PAA hydrogel. For example, new peaks appear at 1700~1800 cm−1 and 1415~1440 cm−1, which are attributed to the -C=O and the carboxylic acid groups, indicating the PAA hydrogel is cross-linked in the CLC PC films. Figure 8c shows the FTIR spectrum of the CLC-PAA hydrogel films immobilized with urease (CLC-PAAurease films). The new peak at 3000~3700 cm−1 represents the amide bands from the urease. Thus, it is obvious that urease was successfully immobilized in the CLC-PAA hydrogel films.

3.4. Optimization of Experimental Conditions

The concentration of urea plays a significant role in the sensitivity of Hg2+ detection. Thus, we investigated the variation of the wavelength value of the maximum reflection peak of the CLC-PAAurease PC films by the immobilized urease (1000 U/mL) with different urea concentrations (Figure 9). It was found that the wavelength value of the maximum reflection peak of the CLC-PAAurease PC films appeared red-shifted, whereas the wavelength value stayed stable at 10 mM, 50 mM, and 100 mM, respectively. Therefore, we fixed the concentration of urea at 10 mM in the subsequent experiments. In addition, we also studied the responses of the CLC-PAAurease PC films in the same observation time (10 min) to the solutions of urea (10 mM) at the different concentrations of urease. Figure 10a shows the UV–Vis spectra of the CLC-PAAurease PC films at different urease concentrations. It can be clearly observed that the wavelength location corresponding to the maximum reflection peak was red shifted (Figure 10b) and the color of the films changed from green to orange with the increasing urease concentration (Figure 10c). It was also revealed that within the investigated concentration range, the response signal of the films reached the platform period when the concentration of urease was greater than or equal to 800 U/mL. Therefore, we chose the concentration of urease at 800 U/mL as the optimal condition.

3.5. Sensitivity and Specificity of CLC-PAA Urease PC Films for Hg2+ Detection

We explored the responses of the wavelength value of the maximum reflection peak coupled to different concentrations of Hg2+ with the prepared CLC-PAAurease PC films (Figure 11a). It is clear that Hg2+ can inhibit the activity of urease, resulting in a change in the microenvironment of the prepared films. It was found that the wavelength value of the reflection spectrum showed an obvious blue shift when increasing the concentration of Hg2+. The wavelength value of the reflected light of the prepared films did not change at 10 nM, which was considered to be the detection limit of Hg2+ (Figure 11b). The color of the film gradually changes from yellow-green to blue (Figure 11c). Finally, we explored the specificity of the prepared films for the detection of Hg2+. As seen in Figure 12, when Hg2+ is present, the changes in the UV-visible reflection spectra wavelength of the CLC-PAAurease PC films are obviously observed compared with the blank and other metal ions. This result clearly reveals the specificity of the proposed method in the detection of Hg2+.

4. Conclusions

In summary, a simple, portable and new strategy has been developed for the detection of Hg2+ based on CLC-PAAurease PC films. The detection limit of Hg2+ is as low as 10 nM. This method immobilized urease on CLC-PAA PC films and changed the optical signal of the prepared films by the enzymatic hydrolysis of urea leading to variation in the microenvironment. The reflected wavelength is directly used as the detection signal of the films. The proposed strategy is very promising in the evaluation of environmental water.

Author Contributions

Conceptualization, resources, supervision, project administration, funding acquisition, L.Y.; methodology, writing—original draft preparation, J.L.; investigation, visualization, W.T.; data curation, formal analysis, J.S.; validation, visualization, D.W. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the National Natural Science Foundation of China (No. 21972074).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

Li Yu acknowledges financial support from the National Natural Science Foundation of China.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Zhou, Z.; Yan, R.; Zhao, J.; Zhao, J.; Yang, L.; Chen, J.; Hu, Y.; Jiang, F.; Liu, Y. Highly selective and sensitive detection of Hg2+ based on fluorescence enhancement of Mn-doped ZnSe QDs by Hg2+-Mn2+ replacement. Sens. Actuators B Chem. 2018, 254, 8–15. [Google Scholar] [CrossRef]
  2. Gao, P.; Lei, J.; Tan, J.; Wang, G.; Liu, H.; Zhou, L. Self-assembled magnetic microcrystalline cellulose/MoS2/Fe3O4 composite for efficient adsorptive removal of mercury ions (Hg2+). Compos. Commun. 2021, 25, 100736. [Google Scholar] [CrossRef]
  3. Mermer, Z.; Yavuz, O.; Atasen, S.K.; Alcay, Y.; Yilmaz, I. Architecture of multi-channel and easy-to-make sensors for selective and sensitive Hg2+ ion recognition through HgC and HgN bonds of naphthoquinone-aniline/pyrene union. J. Hazard. Mater. 2021, 410, 124597. [Google Scholar] [CrossRef] [PubMed]
  4. Tian, C.; Zhao, L.; Zhu, J.; Zhang, S. Ultrasensitive detection of trace Hg2+ by SERS aptasensor based on dual recycling amplification in water environment. J. Hazard. Mater. 2021, 416, 126251. [Google Scholar] [CrossRef]
  5. Song, W.; Xiong, H.; Qi, R.; Wang, S.; Yang, Y. Effect of salinity and algae biomass on mercury cycling genes and bacterial communities in sediments under mercury contamination: Implications of the mercury cycle in arid regions. Environ. Pollut. 2021, 269, 116141. [Google Scholar] [CrossRef]
  6. Ma, M.; Du, H.; Wang, D. Mercury methylation by anaerobic microorganisms: A review. Crit. Rev. Environ. Sci. Technol. 2019, 49, 1893–1936. [Google Scholar] [CrossRef]
  7. Song, C.; Yang, B.; Zhu, Y.; Yang, Y.; Wang, L. Ultrasensitive sliver nanorods array SERS sensor for mercury ions. Biosens. Bioelectron. 2017, 87, 59–65. [Google Scholar] [CrossRef]
  8. Oh, S.; Jeon, J.; Jeong, J.; Park, J.; Oh, E.-T.; Park, H.J.; Lee, K.-H. Fluorescent Detection of Methyl Mercury in Aqueous Solution and Live Cells Using Fluorescent Probe and Micelle Systems. Anal. Chem. 2020, 92, 4917–4925. [Google Scholar] [CrossRef]
  9. Guzzi, G.; Ronchi, A.; Pigatto, P. Toxic effects of mercury in humans and mammals. Chemosphere 2021, 263, 127990. [Google Scholar] [CrossRef]
  10. Lei, Y.; Zhang, F.; Guan, P.; Guo, P.; Wang, G. Rapid and selective detection of Hg(ii) in water using AuNP in situ-modified filter paper by a head-space solid phase extraction Zeeman atomic absorption spectroscopy method. New J. Chem. 2020, 44, 14299–14305. [Google Scholar] [CrossRef]
  11. Hsu, I.H.; Hsu, T.-C.; Sun, Y.-C. Gold-nanoparticle-based graphite furnace atomic absorption spectrometry amplification and magnetic separation method for sensitive detection of mercuric ions. Biosens. Bioelectron. 2011, 26, 4605–4609. [Google Scholar] [CrossRef] [PubMed]
  12. Wang, Z.; Wu, D.; Wu, G.; Yang, N.; Wu, A. Modifying Fe3O4 microspheres with rhodamine hydrazide for selective detection and removal of Hg2+ ion in water. J. Hazard. Mater. 2013, 244, 621–627. [Google Scholar] [CrossRef] [PubMed]
  13. Paglia, G.; Miedico, O.; Tarallo, M.; Lovino, A.R.; Astarita, G.; Chiaravalle, A.E.; Corso, C. Evaluation of seasonal variability of toxic and essential elements in urine analyzed by inductively coupled plasma mass spectrometry. Expos. Health 2016, 9, 79–88. [Google Scholar] [CrossRef]
  14. Shih, T.-T.; Chen, J.-Y.; Luo, Y.-T.; Lin, C.-H.; Liu, Y.-H.; Su, Y.-A.; Chao, P.-C.; Sun, Y.-C. Development of a titanium dioxide-assisted preconcentration/on-site vapor-generation chip hyphenated with inductively coupled plasma-mass spectrometry for online determination of mercuric ions in urine samples. Anal. Chim. Acta 2019, 1063, 82–90. [Google Scholar] [CrossRef] [PubMed]
  15. Surucu, O. Electrochemical removal and simultaneous sensing of mercury with inductively coupled plasma-mass spectrometry from drinking water. Mater. Today Chem. 2022, 23, 100639. [Google Scholar] [CrossRef]
  16. Fu, L.; Zhuang, J.; Tang, D.; Que, X.; Lai, W.; Chen, G. DNA pseudoknot-functionalized sensing platform for chemoselective analysis of mercury ions. Analyst 2012, 137, 4425–4427. [Google Scholar] [CrossRef]
  17. He, W.; Qiao, B.; Li, F.; Pan, L.; Chen, D.; Cao, Y.; Tu, J.; Wang, X.; Lv, C.; Wu, Q. A novel electrochemical biosensor for ultrasensitive Hg2+ detection via a triple signal amplification strategy. Chem. Commun. 2021, 57, 619–622. [Google Scholar] [CrossRef]
  18. Wang, L.; Yang, Y.; Liang, H.; Pan, L.; Chen, D.; Cao, Y.; Tu, J.; Wang, X.; Lv, C.; Wu, Q. A novel N,S-rich COF and its derived hollow N,S-doped carbon@Pd nanorods for electrochemical detection of Hg2+ and paracetamol. J. Hazard. Mater. 2021, 409, 124528. [Google Scholar] [CrossRef]
  19. Qi, J.; Li, B.; Wang, X.; Zhang, Z.; Wang, Z.; Han, J.; Chen, L. Three-dimensional paper-based microfluidic chip device for multiplexed fluorescence detection of Cu2+ and Hg2+ ions based on ion imprinting technology. Sens. Actuators B Chem. 2017, 251, 224–233. [Google Scholar] [CrossRef]
  20. Peng, D.; Zhang, L.; Liang, R.-P.; Qiu, J.-D. Rapid Detection of Mercury Ions Based on Nitrogen-Doped Graphene Quantum Dots Accelerating Formation of Manganese Porphyrin. ACS Sens. 2018, 3, 1040–1047. [Google Scholar] [CrossRef]
  21. Wang, J.; Du, C.; Yu, P.; Zhang, Q.; Li, H.; Sun, C. A label-free and enzyme-free fluorescent assay for mercury ions based on T-Hg(II)-T nanoladders and DNA-templated silver nanoclusters/graphene oxide nanocomposites. Sens. Actuators B Chem. 2021, 348, 130707. [Google Scholar] [CrossRef]
  22. Lim, J.W.; Kim, T.Y.; Choi, S.W.; Woo, M.A. 3D-printed rolling circle amplification chip for on-site colorimetric detection of inorganic mercury in drinking water. Food Chem. 2019, 300, 125177. [Google Scholar] [CrossRef] [PubMed]
  23. Tokunaga, S.; Itoh, Y.; Tanaka, H.; Araoka, F.; Aida, T. Redox-responsive chiral dopant for quick electrochemical color modulation of cholesteric liquid crystal. J. Am. Chem. Soc. 2018, 140, 10946–10949. [Google Scholar] [CrossRef] [PubMed]
  24. Kelly, J.A.; Shukaliak, A.M.; Cheung, C.C.; Shopsowitz, K.E.; Hamad, W.Y.; MacLachlan, M.J. Responsive photonic hydrogels based on nanocrystalline cellulose. Angew. Chem. Int. Ed. 2013, 52, 8912–8916. [Google Scholar] [CrossRef]
  25. Haque, M.A.; Kamita, G.; Kurokawa, T.; Tsujii, K.; Gong, J. Unidirectional alignment of lamellar bilayer in hydrogel: One-dimensional swelling, anisotropic modulus, and stress/strain tunable structural color. Adv. Mater. 2010, 22, 5110–5114. [Google Scholar] [CrossRef]
  26. Seo, H.J.; Lee, S.S.; Noh, J.; Ka, J.-W.; Won, J.C.; Park, C.; Kim, S.-H.; Kim, Y.H. Robust photonic microparticles comprising cholesteric liquid crystals for anti-forgery materials. J. Mater. Chem. C 2017, 5, 7567–7573. [Google Scholar] [CrossRef]
  27. Dierking, I. Chiral Liquid Crystals: Structures, Phases, Effects. Symmetry 2014, 6, 444–472. [Google Scholar] [CrossRef] [Green Version]
  28. Ding, H.; Zhu, C.; Tian, L.; Liu, C.; Fu, G.; Shang, L.; Gu, Z. Structural Color Patterns by Electrohydrodynamic Jet Printed Photonic Crystals. ACS Appl. Mater. Interfaces 2017, 9, 11933–11941. [Google Scholar]
  29. Lim, J.S.; Kim, Y.J.; Park, S.Y. Functional solid-state photonic droplets with interpenetrating polymer network and their applications to biosensors. Sens. Actuators B Chem. 2021, 329, 129165. [Google Scholar] [CrossRef]
  30. Chen, G.; Wang, L.; Wang, Q.; Sun, J.; Song, P.; Chen, X.; Liu, X.; Guan, S.; Zhang, X.; Wang, L.; et al. Photoinduced Hyper-Reflective Laminated Liquid Crystal Film with Simultaneous Multicolor Reflection. ACS Appl. Mater. Interfaces 2014, 6, 1380–1384. [Google Scholar] [CrossRef]
  31. Stumpel, J.E.; Gil, E.R.; Spoelstra, A.B.; Bastiaansen, C.M.; Broer, D.J.; Schenning, A.J. Stimuli-responsive materials based on interpenetrating polymer liquid crystal hydrogels. Adv. Funct. Mater. 2015, 25, 3314–3320. [Google Scholar] [CrossRef]
  32. Chang, C.K.; Kuo, H.L.; Tang, K.T.; Chiu, S.W. Optical detection of organic vapors using cholesteric liquid crystals. Appl. Phys. Lett. 2011, 99, 073504. [Google Scholar] [CrossRef]
  33. Mujahid, A.; Stathopulos, H.; Lieberzeit, P.A.; Dickert, F.L. Solvent vapour detection with cholesteric liquid crystals-optical and mass-sensitive evaluation of the sensor mechanism. Sensors 2010, 10, 4887–4897. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  34. Cho, S.; Li, Y.; Seo, M.; Kumacheva, E. Nanofibrillar Stimulus-Responsive Cholesteric Microgels with Catalytic Properties. Angew. Chem. Int. Ed. 2016, 55, 14014–14018. [Google Scholar] [CrossRef]
  35. Zhang, P.; Kragt, A.J.; Schenning, A.J.; Haan, L.D.; Zhou, G. An easily coatable temperature responsive cholesteric liquid crystal oligomer for making structural color patterns. J. Mater. Chem. C 2018, 6, 7184–7187. [Google Scholar] [CrossRef]
  36. Wani, O.M.; Verpaalen, R.; Zeng, H.; Priimagi, A.; Schenning, A.J. An artificial nocturnal flower via humidity-gated photoactuation in liquid crystal networks. Adv. Mater. 2019, 31, 1805985. [Google Scholar] [CrossRef]
  37. Hussain, S.; Park, S.Y. Optical glucose biosensor based on photonic interpenetrating polymer network with solid-state cholesteric liquid crystal and cationic polyelectrolyte. Sens. Actuators B Chem. 2020, 316, 128099. [Google Scholar] [CrossRef]
  38. Kim, Y.J.; Park, S.Y. Optical Multisensor array with functionalized photonic droplets by an interpenetrating polymer network for human blood analysis. ACS Appl. Mater. Interfaces 2020, 12, 47342–47354. [Google Scholar] [CrossRef]
  39. Myung, D.B.; Hussain, S.; Park, S.Y. Photonic calcium and humidity array sensor prepared with reactive cholesteric liquid crystal mesogens. Sens. Actuators B Chem. 2019, 298, 126894. [Google Scholar] [CrossRef]
  40. Hussain, S.; Park, S.Y. Sweat-based noninvasive skin-patchable urea biosensors with photonic interpenetrating polymer network films integrated into PDMS chips. ACS Sens. 2020, 5, 3988–3998. [Google Scholar] [CrossRef]
  41. Wijayaratna, U.N.; Kiridena, S.D.; Adams, J.D.; Behrend, C.J.; Anker, J.N. Synovial Fluid pH Sensor for Early Detection of Prosthetic Hip Infections. Adv. Funct. Mater. 2021, 31, 2104124. [Google Scholar] [CrossRef]
  42. Jang, J.-H.; Park, S.-Y. pH-responsive cholesteric liquid crystal double emulsion droplets prepared by microfluidics. Sens. Actuators B Chem. 2017, 241, 636–643. [Google Scholar] [CrossRef]
  43. Noh, K.G.; Park, S.Y. Biosensor array of interpenetrating polymer network with photonic film templated from reactive cholesteric liquid crystal and enzyme-immobilized hydrogel polymer. Adv. Funct. Mater. 2018, 28, 1707562. [Google Scholar] [CrossRef]
  44. Jung, S.; Kaar, J.L.; Stoykovich, M.P. Design and functionalization of responsive hydrogels for photonic crystal biosensors. Mol. Syst. Des. Eng. 2016, 1, 225–241. [Google Scholar] [CrossRef]
  45. Yoon, S.; Park, H.; Lee, W. Fabrication of inverse opal photonic gel sensors on flexible substrates by transfer process. Lab Chip 2021, 21, 2997–3003. [Google Scholar] [CrossRef]
  46. Park, H.; Koh, Y.G.; Lee, W. Smartphone-based colorimetric analysis of structural colors from pH-responsive photonic gel. Sens. Actuators B Chem. 2021, 345, 130359. [Google Scholar] [CrossRef]
  47. Cai, Z.; Smith, N.L.; Zhang, J.-T.; Asher, S.A. Two-Dimensional Photonic Crystal Chemical and Biomolecular Sensors. Anal. Chem. 2015, 87, 5013–5025. [Google Scholar] [CrossRef]
  48. Ding, H.; Liu, C.; Ye, B.; Fu, F.; Wang, H.; Zhao, Y.; Gu, Z. Free-Standing Photonic Crystal Films with Gradient Structural Colors. ACS Appl. Mater. Interfaces 2016, 8, 6796–6801. [Google Scholar] [CrossRef]
  49. Fei, X.; Lu, T.; Ma, J.; Wang, W.; Zhu, S.; Zhang, D. Bioinspired Polymeric Photonic Crystals for High Cycling pH-Sensing Performance. ACS Appl. Mater. Interfaces 2016, 8, 27091–27098. [Google Scholar] [CrossRef]
  50. Qin, J.; Dong, B.; Li, X.; Han, J.; Gao, R.; Su, G.; Cao, L.; Wang, W. Fabrication of intelligent photonic crystal hydrogel sensors for selective detection of trace mercury ions in seawater. J. Mater. Chem. C 2017, 5, 8482–8488. [Google Scholar] [CrossRef]
  51. Xiao, F.; Sun, Y.; Du, W.; Shi, W.; Wu, Y.; Liao, S.; Wu, Z.; Yu, R. Smart Photonic Crystal Hydrogel Material for Uranyl Ion Monitoring and Removal in Water. Adv. Funct. Mater. 2017, 27, 1702147. [Google Scholar] [CrossRef]
Figure 1. Schematic diagram of CLC-PAA urease PC films for the detection of Hg2+.
Figure 1. Schematic diagram of CLC-PAA urease PC films for the detection of Hg2+.
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Figure 2. Comparison diagram of PAA gel film in water: (a) before and (b) after the swelling.
Figure 2. Comparison diagram of PAA gel film in water: (a) before and (b) after the swelling.
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Figure 3. Swelling ratio (φ) of PAA gel film (a) at different amounts of TPGDA (ζ) and (b) at different pH. φ is defined as (m2 − m1)/m1, where m2 and m1 are the mass of gel film in water and dry state, respectively.
Figure 3. Swelling ratio (φ) of PAA gel film (a) at different amounts of TPGDA (ζ) and (b) at different pH. φ is defined as (m2 − m1)/m1, where m2 and m1 are the mass of gel film in water and dry state, respectively.
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Figure 4. SEM images of (a) fractured surface and (b) the upper surface of prepared CLC PC films. (c) UV–vis spectra and the optical photographs of Ex-CLC, CLC PC and CLC-PAA PC film.
Figure 4. SEM images of (a) fractured surface and (b) the upper surface of prepared CLC PC films. (c) UV–vis spectra and the optical photographs of Ex-CLC, CLC PC and CLC-PAA PC film.
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Figure 5. SEM images of fractured surface of (a) CLC film and (b) CLC-PAA photonic crystal hydrogel film when the films were cut perpendicularly to the surface of films. scale bar: 1 μm.
Figure 5. SEM images of fractured surface of (a) CLC film and (b) CLC-PAA photonic crystal hydrogel film when the films were cut perpendicularly to the surface of films. scale bar: 1 μm.
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Figure 6. Tensile stress–strain curves of CLC, PAA and CLC-PAA films.
Figure 6. Tensile stress–strain curves of CLC, PAA and CLC-PAA films.
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Figure 7. (a) UV-visible reflection spectra of CLC-PAA PC films at different pH; (b) The wavelengths of the reflection light and the optical images of CLC-PAA PC films under different pH.
Figure 7. (a) UV-visible reflection spectra of CLC-PAA PC films at different pH; (b) The wavelengths of the reflection light and the optical images of CLC-PAA PC films under different pH.
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Figure 8. FTIR spectra of (a) CLC PC films, (b) CLC-PAA PC films, and (c) CLC-PAAurease PC films, respectively.
Figure 8. FTIR spectra of (a) CLC PC films, (b) CLC-PAA PC films, and (c) CLC-PAAurease PC films, respectively.
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Figure 9. UV-visible reflection spectra of CLC-PAAurease photonic crystal hydrogel films after dropping urea solution (200 µL) with different concentrations for 10 min.
Figure 9. UV-visible reflection spectra of CLC-PAAurease photonic crystal hydrogel films after dropping urea solution (200 µL) with different concentrations for 10 min.
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Figure 10. (a) The UV-visible reflection spectra of CLC-PAA PC films at different concentrations of urease (The films were treated with 10 mM urea for 10 min.); (b) The wavelength values of the reflection light; (c) The optical images of CLC-PAA PC films at different concentrations of urease. scale bar: 1 mm.
Figure 10. (a) The UV-visible reflection spectra of CLC-PAA PC films at different concentrations of urease (The films were treated with 10 mM urea for 10 min.); (b) The wavelength values of the reflection light; (c) The optical images of CLC-PAA PC films at different concentrations of urease. scale bar: 1 mm.
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Figure 11. (a) The UV-visible reflection spectra of CLC-PAAurease PC films at different concentrations of Hg2+ (The films were treated with 10 mM urea for 10 min.); (b) The wavelength values of the reflection light of CLC-PAAurease PC films at different concentrations of Hg2+; (c) The optical images of CLC-PAA urease PC films at different concentrations of Hg2+. scale bar: 1 mm.
Figure 11. (a) The UV-visible reflection spectra of CLC-PAAurease PC films at different concentrations of Hg2+ (The films were treated with 10 mM urea for 10 min.); (b) The wavelength values of the reflection light of CLC-PAAurease PC films at different concentrations of Hg2+; (c) The optical images of CLC-PAA urease PC films at different concentrations of Hg2+. scale bar: 1 mm.
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Figure 12. (a) UV-visible reflection spectra of CLC-PAAurease PC films with various metal ions (The films were treated with urea (10 mM) for 10 min); (b) The wavelength values of the reflected light of CLC-PAAurease PC films with various metal ions.
Figure 12. (a) UV-visible reflection spectra of CLC-PAAurease PC films with various metal ions (The films were treated with urea (10 mM) for 10 min); (b) The wavelength values of the reflected light of CLC-PAAurease PC films with various metal ions.
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Liu, J.; Tai, W.; Wang, D.; Su, J.; Yu, L. Cholesteric Liquid Crystal Photonic Hydrogel Films Immobilized with Urease Used for the Detection of Hg2+. Chemosensors 2022, 10, 140. https://0-doi-org.brum.beds.ac.uk/10.3390/chemosensors10040140

AMA Style

Liu J, Tai W, Wang D, Su J, Yu L. Cholesteric Liquid Crystal Photonic Hydrogel Films Immobilized with Urease Used for the Detection of Hg2+. Chemosensors. 2022; 10(4):140. https://0-doi-org.brum.beds.ac.uk/10.3390/chemosensors10040140

Chicago/Turabian Style

Liu, Jie, Wenjun Tai, Deliang Wang, Jie Su, and Li Yu. 2022. "Cholesteric Liquid Crystal Photonic Hydrogel Films Immobilized with Urease Used for the Detection of Hg2+" Chemosensors 10, no. 4: 140. https://0-doi-org.brum.beds.ac.uk/10.3390/chemosensors10040140

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