Molecularly Imprinted Ratiometric Fluorescent Sensors for Analysis of Pharmaceuticals and Biomarkers
Abstract
:1. Introduction
2. Fluorescent Signal Source and Working Mechanism of MI-RFL Sensor
2.1. Fluorescent Signal Source
2.1.1. Fluorescent Dyes
2.1.2. Quantum Dots
2.1.3. Upconversion Nanoparticles
2.1.4. Metal Nanoclusters
2.2. Working Mechanism of MI-RFL Sensor
2.2.1. FRET
2.2.2. IFE
2.2.3. PET
2.2.4. Other Mechanisms
3. New Techniques and Strategies for the Preparation of MIPs
3.1. Surface Imprinting Technology
3.2. Nanoimprinting Technology
3.3. Dummy Imprinting Strategy
3.4. Multi-Template Imprinting Strategy
3.5. Stimulus-Response Imprinting Strategy
4. Types of Fluorescence Emission from the MI-RFL Sensor
5. Application of MI-RFL Sensors in Analysis of Pharmaceuticals and Biomarkers
5.1. Pharmaceutical Analysis
5.1.1. Detection of Veterinary Drug Residues
- Antibiotics
- 2.
- Hormones
5.1.2. Detection of Pesticide Residues
- Insecticides
- 2.
- Herbicides
- 3.
- Bactericides
5.1.3. Pharmaceuticals for Human Use
- Natural Organic Compounds and TCM
- 2.
- Synthetic Pharmaceuticals
5.2. Biomarkers Analysis
5.2.1. Proteins
5.2.2. Nucleotides
5.2.3. Amino Acids
6. Application of MI-RFL Sensors for POCT
6.1. Test Strips
6.2. Smartphones
6.3. Microfluidic Chips
7. Conclusions and Prospects
- (1)
- Sensor construction and optimization: The application of MI-RFL sensors in pharmaceuticals and biomarkers detection depends on their efficient, sensitive, and selective performance, and the optimization of the construction process is critical to achieve these performances. The construction process of MI-RFL sensor mainly includes the selection of fluorescence signal sources and the preparation of MIPs.
- (i)
- Selection of fluorescence source: Although traditional fluorescent dyes and nanomaterials have been widely used, issues such as stability, spectral overlap, toxicity, and cost still need to be addressed. Cyanine dyes have excellent photostability, wide spectral range, and tunable fluorescence characteristics. Meanwhile, the relatively high quantum yield of cyanine dyes helps to improve the detection sensitivity of the sensor. These advantages make it potential for application in the field of MI-RFL sensors [129,130]. Therefore, the development of fluorescent dyes, such as cyanine dyes, and new fluorescent materials, such as BU-MOFs, and the optimization of their optical properties through surface modification, doping, and recombination become an important direction of future research. At the same time, the integration strategy of multiple fluorescence sources is also expected to achieve effective cooperation between different sources and improve the detection accuracy.
- (ii)
- Selection of reaction mechanism: In practical applications, the appropriate reaction mechanism should be selected according to the specific detection requirements and the nature of the target molecules. For drugs or biomarkers with specific structures and properties, mechanisms such as FRET, PET, and ICT can be selected to achieve highly selective and responsive detection by designing specific fluorescent probes and receptors. In the pursuit of rapid detection, the IFE mechanism is more advantageous because it does not require a complex energy transfer process and can respond to the target faster. For high sensitivity detection requirements, PET and AIE mechanisms may perform better, which achieve significant fluorescence changes at low concentrations [131]. Furthermore, the combination of multiple reaction mechanisms and sensor design strategies can improve the performance and applicability of the sensors. In the future, with deepening understanding of different reaction mechanisms, reaction mechanisms can be precisely selected and designed to further improve the performance of MI-RFL sensors [132].
- (iii)
- Preparation of MIPs: The MIPs preparation process was optimized, including the selection of template molecules, polymerization conditions of functional monomers, type and dosage of cross-linking agents, and others, which could significantly improve the performance of the sensor. In addition, the introduction of dummy templates, multi-template strategies, and new imprinting methods, such as electrochemical imprinting and light-controlled imprinting, also provide the possibility to further improve the performance of sensors. The application of theoretical calculations during the preparation of imprinted materials will be an important research direction. For example, Chi et al. [133] used density functional theory (DFT) to calculate the binding energy and molecular electrostatic potential of template molecules and functional monomer complexes and fabricated an MI-RFL sensor with excellent performance for the detection of mycotoxins in food under the guidance of theoretical calculations. This example shows that by simulating the interaction between template molecules and functional monomers, the optimal polymerization conditions can be determined. Then the performance of MI-RFL sensors can be effectively improved. In the future, theoretical computing will also have broad application prospects in the field of pharmaceuticals and biomarkers, providing strong technical support for accurate detection, precise diagnosis, and treatment.
- (2)
- Introduction of new functional materials: The introduction of new functional materials, such as MOFs, covalent organic framework (COFs), and hydrogen-bonded organic framework (HOFs) can bring higher sensitivity and selectivity to MI-RFL sensors. These materials have unique physicochemical properties, such as high specific surface area, tunable pore size, and excellent chemical stability, which can significantly enhance the performance of the sensors. Currently, MOFs are widely used in the construction of MI-RFL sensors, while COFs are relatively less used. This is because COFs have some problems, such as their strong π–π stacking interactions, which lead to quenching effects, and their synthesis is difficult and requires strict reaction conditions, while there are also problems in stability and compatibility in practical application scenarios [134,135]. HOFs are still in their infancy, and their applications are limited. On the one hand, due to the late start of their research, people’s understanding of their physicochemical properties and application potential is not comprehensive. On the other hand, HOFs are ordered porous materials formed by intermolecular hydrogen bonding assembly. Their structural stability is easily affected by surrounding factors, and they face many technical difficulties in achieving high selectivity for specific analytes, which is the main reason why their development lags far behind other porous materials such as MOFs and COFs [136,137]. In the future, with the deepening of research on MOFs, COFs, and HOFs, these materials will play a greater role in the fields of biosensing, environmental monitoring, and drug delivery.
- (3)
- Currently, the research on dual-emission MI-RFL sensors is relatively mature, while the research on triple-emission ratiometric fluorescence sensors is still insufficient but has great potential. PIMix and PIMod, as an ideal construction strategy, effectively enhance the sensor performance by optimizing the material ratios and surface modification. However, the triple-emission technology also faces the problems of complicated preparation process, high cost, and stability issues, such as fluorescence intensity attenuation of multiple emission peaks and shifting of emission peaks, which need to be solved by subsequent research. In the future, it is expected that the triple-emission ratiometric fluorescent sensors will be further developed in the field of pharmaceuticals and biomarkers analysis.
- (4)
- At present, the application and research of MI-RFL sensors in the field of green imprinting technology is in the embryonic stage but has shown great potential and broad prospects to lead the trend of greening chemical sensors in the future. Green imprinting technology not only runs through the entire life cycle of MI-RFL sensors from design, preparation, to use, but also aims to significantly reduce chemical waste, lower energy consumption, and significantly improve the environmental friendliness of the sensors through environmentally friendly and sustainable strategies.
- (5)
- In the field of pharmaceuticals and biomarkers analysis, MI-RFL sensors, although showing advantages such as high selectivity and sensitivity, still face many challenges. The main challenges include improving the sensor’s immunity to interference in complex samples, optimizing the material preparation process to ensure reproducibility, and overcoming the difficulty of template molecule removal. In addition, there is a need to further improve the selectivity and sensitivity of MI-RFL sensors for detecting trace residues in complex matrices, as well as to effectively overcome the interference caused by matrix effects, to enhance their ability to detect target molecules at low concentrations. Therefore, future technological innovation will be the key, including the introduction of new functional materials, optimization of the sensor structure, simplification of the sample pre-treatment process, and realization of multi-component simultaneous detection and so on, which will promote the wide application of MI-RFL sensors in the field of pharmaceutical analysis.
- (6)
- Current MI-RFL sensors have been closely integrated with POCT technology to achieve more convenient and visualized on-site detection. Through the integration with smartphones, test strips, microfluidic paper chips, and other technologies, the sensor can perform rapid and accurate testing directly on-site, which greatly improves testing efficiency and convenience. In the future, with the continuous progress of machine learning and theoretical calculation technologies, MI-RFL sensors are expected to achieve deep integration with these advanced technologies on the existing basis to further improve the detection accuracy and intelligence. This will provide more efficient and accurate solutions for medical and healthcare, environmental monitoring, and other fields.
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Type | Analyte | Fluorescence Sources | Functional Monomer | Crosslinker | Polymerization Method | Working Mechanism | Imprinting Strategy | Linear Range | LOD | Real Sample | Recovery (%) | RSD (%) | Ref. |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Pharmaceuticals analysis | NOR | CDs | MAA | EDGMA | – | ICT | Surface imprinting | 5–50 nM | 1.35 nM | Tap water, river water | 93–106.8 | 2.0–3.6 | [79] |
DOX | CdTe QDs | APTES | TEOS | Sol–gel method | IFE | Dummy template imprinting | 0.1–50 μM | 0.061 μM | Seawater, reservoir water, urine | 91.6–107.5 | 2.9–4.6 | [80] | |
CDs | APTES | TEOS | Sol–gel method | AIE, IFE | – | 0.05–20 mg/L | 14.21 ng/mL | Lake water, milk | 90.16–97.18 | <4.77 | [53] | ||
TC | WO3-x QDs | MAA | EDGMA | – | PET, IFE | – | 0.01–10.0 μmol/L 20.0–80.0 μmol/L | 3.23 nmol/L and 6.37 μmol/L | Milk, egg | 92.7–102.9 | <1.59 | [81] | |
CDs | APTES | TEOS | Sol–gel method | ET | – | 25–2000 nM | 7.9 nM | Milk | 94.2–103.7 | 1.5–5.3 | [82] | ||
QDs | AM | EGDMA | Precipitation polymerization | ET | – | 10–160 μmol/L | 0.35 μmol/L | Milk | 96.3–106.2 | 1.9–4.3 | [83] | ||
CDs | AM | EGDMA | – | ET | Surface imprinting | 0–50 nM | 1.19 nM | River water, tap wate | 99.13–102.75 | 0.67–0.98 | [38] | ||
SDZ | CDs | 4-VP | MBAAM | – | ET | – | 2–20 μmol/L | 4.2 nmol/L | Lake water, tap water | 94.1–96.5 | 1.6–3.4 | [84] | |
CdTe QDs | AM | MBAAM | – | – | – | 0–100 μmol/L | 11 nmol/L | Tap water, lake water | 92.0–95.1 | <3.6 | [85] | ||
FZD | CNDs | AMPS | EDGMA | Suspension polymerization | IFE | – | 5–400 mg/L | 1.98 mg/L | Chicken feed, honey, pork | 90–110 | <3.7 | [39] | |
CAP | QDs | APTES | TEOS | Sol–gel method | PET | Stimuli-responsive | 0.015–0.12 nM 0.12–17.22 nM | 0.009 nM | Lake water, chicken, fish, human urine | 94.0–108.0 | 2.1–4.2 | [68] | |
NH2-UiO-66, CdTe QDs | APTES | TEOS | Sol–gel method | PET | – | 10 pM–0.5 nM 0.5 nM–4.5 nM | 3.8 pM | Meat, milk, honey | 98.2–101.2 | 2.1–3.6 | [86] | ||
CIP | CdTe QDs, CDs | APTES | TEOS | Sol–gel method | ET | – | 0.5–20 μM | 0.09 μM | Seawater | 96.2–103.1 | 0.85–2.89 | [87] | |
TAP | CDs | APTES | TEOS | Sol–gel method | PET | – | 5.0 nM–6.0 μM 6.0 μM–26.0 μM | 50 μg/kg | Fish, shrimp, beef, milk | 95.0–105.0 | 3.1–4.5 | [88] | |
PNG | CDs | APTES | TEOS | Sol–gel method | EF | – | 1–32 nM | 0.34 nM | Milk | 98–103 | <0.9 | [89] | |
CLP | CDs | APTES | TEOS | Sol–gel method | ET | _ | 0.1–3 μg/L | 0.035 μg/L | Milk | 96.5–106.6 | 1.1–3.5 | [90] | |
DMZ | CDs, CdSe | APTES | TEOS | Sol–gel method | – | – | 0.06–14.1 μg/mL | 47 pg/mL | Pork, honey, eggs | 98.0–104.0 | <3.9 | [91] | |
KS | QDs | APTES | TEOS | Sol–gel method | ET | – | 3.00–105 μM | 0.24 μM. | River water | 102.5–112.6 | 1.12–3.85 | [92] | |
SS | QDs | APTES | TEOS | Sol–gel method | ET | – | 3.00–118 μM | 0.22 μM. | River water | 97.7–106.6 | 2.17–6.21 | [92] | |
E2 | CdTe QDs | APTES | TEOS | Sol–gel method | PET | Surface imprinting | 0.011–50 μg/L | 3.3 ng/L | Tap water, river water, seawater, milk | 92.4–110.6 | <2.5 | [93] | |
IMA | QDs | APTES | TEOS | Sol–gel method | PET | – | 5.0–80.0 μM | 1.4 μM | Puerariae Lobatae Radix, soil | 85.5–98.0 | <4.2 | [94] | |
DEL | CdSe/ZnS QDs | APTES | TEOS | _ | _ | – | 0.01–40.0 mg/L | 1.34 µg/L | Aquatic products, seawater | 98.5–109.0 | <7.5 | [36] | |
Mal | N-CDs, Eu-MOF | APTES | TEOS | Sol–gel method | – | – | 1–10 μM | 0.05 μM | Lettuce, tap water, soil | 93.0–99.3 | <3.1 | [95] | |
1-NP | QDs | APTES | TEOS | – | PET | – | 6.0–140.0 μM | 0.45 μM | Lycium barbarum, Dendrobium officinale | 94–105 | <4.41 | [93] | |
Propazine | QDS | APTES | TEOS | Sol–gel method | PET | – | 0.005–2.000 mg/L | 0.001 mg/L | Seawater, fish | 92.0–114.6 | <6.3 | [96] | |
2,4-D | CdTe QDs, NBD | 4-VP | EGDMA | – | – | Surface imprinting | 0−25 μM | 0.13 μM | Drinking water, lake water, urban runoff water, paddy field water | 99.2–100.8 | 1.5–3.3 | [97] | |
NBD | APTES | TEOS | Sol–gel method | PET | Surface imprinting | 0.1–3 μM | 0.023 μM | River water, tap water | 94–108 | <5 | [32] | ||
CdTe QDs | 4-VP | EGDMA | – | – | Surface imprinting | 0–25 μM | 0.12 μM | Milk | 96.0–104.0 | ≤4.0 | [98] | ||
CdTe QDs, NBD | APTES | TEOS | Sol–gel method | FRET | Surface imprinting | 0.56–80 μM | 90 nM | Soybean sprouts, lake water | 86.2–109.5 | <4.19 | [78] | ||
CdTe QDs, NBD | 4-VP | EGDMA | – | – | Surface imprinting | 0−15 μM | 0.13 μM | Milk | 96.0−103.2 | 1.5−5.5 | [99] | ||
CdTe QDs, | APTES | TEOS | – | ET | Surface imprinting | 0.51–80 μmol/L | 0.17 μmol/L | Cucumber | 96.6–104.2 | 5.5–6.1 | [100] | ||
CDs, FBM | APTES | TEOS | Sol–gel method | PET, IFE | – | 1.0 × 10−12−1.2 × 10−9 M | 7.5 × 10−13 M | River water, grass, cabbage, apple | 7.1−103.3 | 1.3–2.7 | [101] | ||
IDP | QDs | APTES | TEOS | – | ET | – | 5 ng/mL–0.5 μg/mL | 3.55 ng/mL | River water and corn | 97.64–109.88 | 1.00–4.65 | [73] | |
TMX | CDs | APTES | TEOS | Sol–gel method | – | – | 0.05–25 μM | 13.5 nM | Fruit, Chinese cabbages, river water | 91.40–105.7 | 1.64–3.49 | [102] | |
LC | CDs | APTES | TEOS | – | ET | Surface imprinting | 1–150 μg/L | 0.048 μg/L | Tap water, tea, cucumber, apple | 87.93–101.4 | 1.5–5.1 | [103] | |
CF | SiO2@Y2O3:(Eu3+, Tb3+) | MAA | DMAEA | Sol–gel method | FRET, PET | _ | 10–100 μg/ml | 4 μg/ml | Rhubarb, wolfberry | 85.7–92.2 | <3 | [41] | |
Pretilachlor | QDs | APTES | TEOS | Microemulsion polymerization | PET | Surface imprinting | 0.001–5.0 mg/L | 0.05 μg/L | Fish, river water | 92.2–107.6 | <6.5 | [104] | |
Difenoconazole | CDs, NBD | APTES | TEOS | Sol–gel method | PET | Surface imprinting | 0.3~60 μmol/L | 75 nmol/L | Tomato | 102.1–111.2 | 3.1–4.2 | [55] | |
CDs, CdTe QDs | APTES | TEOS | – | IFE | – | – | 0.18 μg/mL | Cucumber | 102.2–108.8 | 4.7–5.6 | [105] | ||
FA | CdTe QDs | APTES | TEOS | Sol–gel method | – | Surface imprinting | 0.05–50 ppm | 0.005 ppm | FA tablets, milk powder | 89.39–103.43 | <3.37 | [76] | |
QDs | APTES | TEOS | Sol–gel method | PET | – | 0.01–50 ppm | 0.0052 ppm | Milk powder, folic acid tablets, porcine serum | 99.5–108.0 | <3.0 | [75] | ||
CdTe QDs, | APTES | TEOS | Sol–gel method | PET | Surface imprinting | 0.23–113 μM | 48 nM | Pinach, broccoli, tomatoes, oranges | 94.8–104.2 | – | [59] | ||
AAs | QDs | APTES | TEOS | Sol–gel method | PET | Multi-Template Imprinting | 24–1200 nM | 9.58 nM | Asarum | 90.10–97.62 | 1.3–2.4 | [106] | |
ME | QDs | APTES | TEOS | Sol–gel method | IFE | Multi-Template Imprinting | 17.1–343 nM | 6.46 nM | Asarum | 97.82–107.93 | 1.3–4.0 | [106] | |
AAI | CDs | 4-VP | EGDMA | – | PET | 1.0–120.0 μmol/L | 0.45 μmol/L | Asarum | 5.5–107.3 | 2.0 | [107] | ||
MTX | CDs | APTES | TEOS | Copolymerization | IFE | – | 5–2000 ng/mL | 1.5 ng/mL | Rabbit plasma, parenteral | 97.80–99.20 | 1.28–2.53 | [108] | |
DA | QDs, CDs | AM, VPBA | MBAAM | Precipitation polymerization | – | – | 0–600 nM | 12.35 nM | Human serum | 98.02–104.06 | <4.45 | [109] | |
DA | CdTe QDs | VPBA | MBAAm | – | ET | Surface imprinting | 0–1.2 × 10−6 M | (100–150) × 10−9 M | Human serum | 100.14–104.46 | <5 | [110] | |
CTD | CDs | APTES | TEOS | Sol–gel method | ET | Surface imprinting | 0.5–1000 nM | 0.15 nM | Blood | 96.12–107.40 | 2.87–3.96 | [111] | |
AA | CdTeS QDs, ZnCdS QDs | APTES | TEOS | Sol–gel method | ET | – | 1–500 μM | 0.78 μM | Vitamin C tablets | 96.0–99.0 | <1.7 | [112] | |
CuNCs, CDs | APTES | TEOS | Sol–gel method | – | Surface imprinting | 4.0–22.0 μM | 1.56 μM | Vitamin C tablet, human serum | 81.69–106.11 | 0.10–0.44 | [44] | ||
ACO | FeS2 QDs | MAA, AM | EDGMA | Sol–gel method | ET | – | 0.05–5.0 μM | 24 nM | Fuzi Lizhong Pills | 95.2–103.1 | <5.0 | [66] | |
Metronidazole | CDs | APTES | TEOS | Sol–gel method | – | – | 25–1000 nmol/L | 7.2 nmol/L | Honey | 92.3–95.1 | 2.5–4.6 | [113] | |
Biomarkers analysis | Histamine | QDs | APTES | TEOS | Sol–gel method | PET | – | 1–60 μM | 21.9 nM | Mackerel, frozen atlantic cod, canned tuna | 96.52–105.32 | 1.57–5.57 | [114] |
AD | BA-EuMOFs | – | TEOS | – | FRET | Surface imprinting | 1–50 mg/L | 0.26 mg/L | Human urine | 96.11–101.79 | <2.87 | [115] | |
BSA | QDs | APTES | TEOS | Sol–gel method | PET | – | 2–64 μM | 0.5 μM | Milk, power milk, human serum, bovine calf serum | 95.9–104.8 | <4 | [16] | |
L-Tyr | CdTe QDs | APTES | TEOS | Sol–gel method | IFE | Surface imprinting | 1.0 × 10–10–2.5 × 10−8 M | 8.0 × 10−11 M | Urine, serum | 99.07–101.18 | 2.00–3.57 | [17] | |
dsDNA | QDs | APTES | TEOS | Sol–gel method | PRET | Surface imprinting | 0.089–1.79 μg/mL | 19.48 ng/mL | Urine | 102.6–106.0 | 2.07–3.15 | [26] | |
CNP | NBD, CDs | APTES | TEOS | Sol–gel method | PET | Surface imprinting | 5–80 pg/mL | 2.87 pg/mL | Human serum | 97.3–104 | <4.7 | [116] | |
BHb | CdTe QDs | APTES | TEOS | Sol–gel method | PET | Surface imprinting | 0.025−3 μM | 7.8 nM | Urine | 99.25−111.7 | <3.2 | [117] | |
PE | CDs | APTES | TEOS | – | FRET | Surface imprinting | 5–200 ng/mL | 1.5 ng/mL | Human serum | 95.94–104.26 | 1.62–4.65 | [49] |
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Yan, J.; Liu, S.; Sun, D.; Peng, S.; Ming, Y.; Ostovan, A.; Song, Z.; You, J.; Li, J.; Fan, H. Molecularly Imprinted Ratiometric Fluorescent Sensors for Analysis of Pharmaceuticals and Biomarkers. Sensors 2024, 24, 7068. https://doi.org/10.3390/s24217068
Yan J, Liu S, Sun D, Peng S, Ming Y, Ostovan A, Song Z, You J, Li J, Fan H. Molecularly Imprinted Ratiometric Fluorescent Sensors for Analysis of Pharmaceuticals and Biomarkers. Sensors. 2024; 24(21):7068. https://doi.org/10.3390/s24217068
Chicago/Turabian StyleYan, Jingyi, Siwu Liu, Dani Sun, Siyuan Peng, Yongfei Ming, Abbas Ostovan, Zhihua Song, Jinmao You, Jinhua Li, and Huaying Fan. 2024. "Molecularly Imprinted Ratiometric Fluorescent Sensors for Analysis of Pharmaceuticals and Biomarkers" Sensors 24, no. 21: 7068. https://doi.org/10.3390/s24217068