Mirinal Kumar
Rayappa
a,
Kavya
K. S.
a,
Gurdeep
Rattu
ab and
P. Murali
Krishna
*a
aDepartment of Basic and Applied Sciences, National Institute of Food Technology Entrepreneurship and Management (NIFTEM), Haryana 131028, India. E-mail: physicsres.niftem@gmail.com
bNational Horticulture Research and Development Foundation (NHRDF), Nashik-Aurangabad Road, Nashik, Maharashtra 422003, India
First published on 18th February 2023
Antibiotic residues in foods are a global threat and one of the main reasons for the antibiotic resistance development in bacteria as reported by WHO and many other agencies. Antibiotics are used for the prevention and treatment of various diseases in humans and animals. They are employed to improve the growth rate and feed efficiency in livestock predominantly. The global antibiotic usage in food animals including aquaculture is increasing rapidly and is estimated to increase by 67% by 2030. Due to a lack of adherence to proper dosage protocols, various antibiotic residues have become increasingly prevalent in food products obtained from livestock that are meant for human consumption. Moreover, these complex antibiotic residues can cause chronic toxicity resulting in public health and environmental crises. Hence it is important to detect these residues in the food supply chain for food safety and public health. Metal–organic frameworks (MOFs) are a class of porous hybrid nanomaterials formed by networks of inorganic metal ions or metal clusters with mono-, bi-, and multi-dentate interlinked organic pliable electron-donating ligands and/or linkers. Owing to their atomic-level structural uniformity, tunable porosity, high surface area, flexibility in network topology, high density of active chemical sites, high chemical catalytic activity, etc., these MOF-based nanomaterials can exhibit unique physical, chemical, and mechanical properties highly useful for sensing platforms. Developing nanomaterial-based sensors to identify and detect major antibiotic residues like beta-lactams, tetracyclines, macrolides, aminoglycosides, amphenicols, etc., in consumer foods is of growing interest and MOF nanomaterial-based optical or electrochemical transduction sensors have been reported to show promising performance for antibiotic residue detection as an alternative to conventional techniques. Thus, this review presents the different classes of MOF-based nanomaterials and their synthesis, structure, functionalization, and sensing methodology to design a robust antibiotic residue detection sensor mainly useful in the food sector (including water). The discussions also extend to challenges and future research to be conducted to make these materials suitable for rapid testing of food samples along the food supply chain to establish a safer, secure, and sustainable food system.
Antibiotic classes | Examples used in livestock |
---|---|
Aminoglycosides | Gentamicin, neomycin |
Macrolides | Erythromycin, tilmicosin, lincomycin, tulathromycin, tylosin |
β-lactams | Penicillin, ceftiofur, amoxicillin |
Fluoroquinolones | Ciprofloxacin, danofloxacin, enrofloxacin |
Tetracyclines | Chlortetracycline, oxytetracycline, tetracycline |
Amphenicols | Chloramphenicol, florfenicol |
Sulfonamides | Various sulfonamides |
Nitrofurans | Nitrofurantoin |
In a study carried out in Nepal, out of milk collected from three different sources (farmers, cottage dairies, and large dairy plants), 81% of samples showed residues of amoxicillin, 27% for penicillin, and 12% for ampicillin.11 Penicillin-G residue was also detected in 41.1% fresh milk, 40.2% fermented milk, and 24.4% cheese.12 Similarly in Bangladesh, penicillin, tetracycline, and ciprofloxacin were found in both milk and eggs.13 Oxytetracycline residues were also found in milk collected in Kerala, India.14
Epidemiological and toxicological studies have concluded that the ingestion of antibiotic residues can result in increased health risks for all age groups resulting in immunopathological effects, carcinogenicity, mutagenicity, nephropathy, hepatotoxicity, reproductive disorders, and even chronic toxic effects due to prolonged low-level exposure.3,10 Apart from these ill effects, exposure to these residues will in-directly give rise to antibiotic-resistant bacteria with antibiotic-resistant genes that can cause greater harm to humankind.15,16 This will also cause current antibiotic therapy to treat various diseases in humans to become a failure and the World Health Organization (WHO) has also declared it a global threat.17,18 Also, the prevalence of these residues in the environment will enable environmental microbiome selection pressure (through horizontal transfer of antibiotic-resistant genes among microbes), thereby resulting in the creation of an antibiotic-resistant gene reservoir thus contributing towards a global environmental antibiotic-resistance to pathogens.8 International bodies like WHO, the Food and Agriculture Organization of the United Nations (FAO), and the World Organization for Animal Health (OIE) are actively monitoring the timely scientific assessment of these antibiotic residues prevalence. In agreement with the WHO and CODEX, the Food Safety and Standards (FSSAI-India) issued mandatory regulations that all animal food products must be tested before their sales in the market. Furthermore, all the food business operators (FBOs) need to check for maximum permissible limits (MRLs) and should mention them on their food packaging labels. Table 2 summarizes the major antibiotic residues and their MRL in foods.
Antibiotics | Foods | FSSAI MRL (mg kg−1) | CODEX AND FAO MRL (mg kg−1) |
---|---|---|---|
Amoxicillin | Milk | — | 0.0004 |
All other tissues | — | 0.005 | |
Ampicillin | All foods | 0.01 | 0.005 |
Streptomycin | Muscle | 0.6 | — |
Liver | 0.6 | — | |
Kidney | 1 | — | |
Fat | 0.6 | — | |
Milk | 0.2 | — | |
Tetracyclines | Muscles | 0.2 | 0.2 |
Liver | 0.6 | 0.6 | |
Kidney | 1.2 | 1.2 | |
Milk | 0.1 | 0.1 | |
Eggs | 0.4 | 0.4 | |
Honey | 0.005 | ||
Erythromycin | Muscles | 0.1 | 0.1 |
Liver | 0.1 | 0.1 | |
Kidney | 0.1 | 0.1 | |
Fats | 0.1 | 0.1 | |
Eggs | 0.05 | 0.05 | |
Sulfonamides | All foods | 0.01 | 0.1 |
Milk | — | 0.025 | |
Chloramphenicol | All food | 0.0003 | Should not be permitted |
Nitrofurans | All foods | 0.0001 | Should not be permitted |
Conventional techniques like HPLC, ELISA, LC-MS, thin-layer chromatography (TLC), time-of-flight mass spectrometry (TOF-MS), microbial assay, capillary electrophoresis (CE), etc., used for antibiotic residue quantification have issues such as being expensive per lab test, requiring a time-consuming procedure, trained personnel, central laboratory facilities, etc.19 Biochemical sensors are seen as an alternative to these quantification methods since they are easy to handle, less expensive, portable, and rapid. These sensor are essentially a self-contained, integrated analytical tool that is used to quantify a target molecule of interest by making use of specific bio- or chemical receptors that are in proximity or are connected to a transduction system.19 In this way, advanced nanomaterials have been used for the detection and quantification of low molecular weight organic and bio-macromolecular compounds and have eventually given rise to rapid, sensitive, portable, and on-site sensing choices.
Recently metal–organic framework (MOF) nanocomposites have gained interest in bio/chemical sensor development due to their specific properties and highly selective detection within and beyond the MRL detection ranges. MOFs make brilliant candidates for sensing applications due to many excellent features they offer such as controllable synthesis, reversible adsorption, high catalytic activity, tunable chemical functionalization, diverse structural constructability, large surface areas, high porosity, thermal stability, ability to be loaded with a high concentration of analytes and high compatibility with respective coordination elements.20–22 A wide range of linkers can be incorporated into MOFs and multiple metals can also be used to synthesize MOF structures. MOFs have a large surface area that is comparable to that of zeolites with multi-size pore structures, which helps in easier capture of analytes during analysis. Post-synthesis modification can also be carried out to change the physical and chemical properties of MOFs.23 MOF-based sensors are less harmful to the environment as they use far fewer hazardous chemicals compared to chromatographic techniques. Hence, there is growing research interest in the development of MOF nanomaterial-based sensors to detect different analytes such as environmental pollutants, antibiotics, VOCs, heavy metals, and other gaseous compounds.24
Despite many papers that have focused on antibiotic detection using various materials, a focused review on MOFs as nanomaterials for antibiotic residue detection in food (including water) with recent advancements is timely and of need. Xenobiotic agents (synthetic chemical substances that are not naturally present in an organism) such as these antibiotic residues are contaminants that are inherently not present in food and are vertically and horizontally transferred across the agro-food chain starting from livestock and agro sources to the natural environment and human consumption products. Such prevalence requires routine monitoring by chemically testing food samples at critical control points (such as testing the food products right before packaging them for retail at food establishments or at a mobile laboratory facility utilizing portable systems for facile testing across livestock farmlands) before sending them across the market for direct human purchase and consumption. Such testing will result in rejecting raw materials right before they are extensively distributed across the supply chain thereby establishing risk-based monitoring with flexible sampling. Therefore, as opposed to conventional high-end central laboratory instruments that are known to identify accurate levels of these residues in food, the alternative material must possess such relative properties to detect the same at least at the lowest levels far below the MRL if not at exact trace level-fingerprinting. With such views, this paper presents a brief narrative of the current scenario of commonly present veterinary antibiotic residues in food followed by a discussion on novel MOF nanomaterial synthesis, their structures, surface modification, and their sensing of these residues by means of optical and electrochemical detection mechanisms in food samples. Further discussions about impediments to using MOFs, and their improvements for antibiotic residue detection in animal-derived food and an emphasis on plant-derived food have also been presented for routine chemical analysis of these residues. Fig. 1 gives an overview of sensing applications in a food chain for detecting veterinary antibiotic residues.
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Fig. 1 Sources of antibiotic residues in foods and their detection using sensors at critical control points within a food chain. |
• Modification of specific organic ligands or doping of metal ions into the frame of MOFs.23,27
• Post-synthesis modification, in which the organic linkers with functional groups can be used for subsequent chemical grafting.27,28
• Entrapment of functional molecules and nanoparticles (NPs) within the framework, so that the resulting composites come to possess multiple functionalities for molecular recognition and signal transduction.27
Many methods including sonochemical, solvothermal, microwave, hydrothermal, and microemulsion methods have been employed in the synthesis of MOF nanoparticles. The most common is the solvothermal method that produces MOFs with a particle size between 300 and 800 nm. It is effective in synthesizing MOFs of varying sizes, as well as controlling the size with control modulators. Therefore, the addition of various modulators of varying concentrations affects the size of the resulting MOF. Xia et al. synthesized ZIF-67 crystals of varying sizes using different solvents (modulators) such as ethanol (bulk), deionized water, and methanol under conditions of 120 °C (3 days) and 60 °C (20 h) respectively.29 Rapid synthesis and nucleation can be accomplished through microwave synthesis. This in turn can help in size reduction. A 104 nm size nano-cubic crystal was synthesized with the microwave method in less than 2 minutes.30 Microemulsion can also facilitate rapid synthesis and effective size reduction. MOFs in quantum dot structures (less than 2 nm) have also been able to be synthesized.31 Rapid kinetics, nucleation, and phase control are also possible in the sonochemical approach. The ultrasonic wave increases the temperature and pressure of the solution through the growth and collapse of the acoustic cavity. Li et al. synthesized MOF NPs of 200–400 nm using a sonochemical approach.32
Nanorods, nanowires, and nanotubes are 1-dimensional structures that are synthesized by controlled synthesis using polycarbonate membranes e.g. ZIF-8. More research can be conducted to utilize these 1-D structures for antibiotic detection, which is very scarce.33,34 While many nanosheet and nanofilm structured MOF attempts have been conducted for the synthesis of 2D MOFs, most reports exist for wide 3D geometric MOF sensor development for antibiotic residue detection.35 Of these, porous MOFs have been shown to be very apt for the absorption and detection of antibiotic residues in food36 based on a variety of network modifications in both 2D and 3D models with high porosity, high ion exchange, and adsorptive properties. This high level of properties could be achieved by intermolecular interactions and metal–ligand coordination.
In contrast to existing materials such as metal oxides, others like porous metal membranes, nanostructured thin films, and conducting polymer MOFs have a high surface area, which provides a large concentration of chemical recognition active sites. Although high porosity can enhance the above-mentioned properties, MOFs still have strong nonspecific adsorption forces that retain other small molecules under ambient conditions due to their porosity. This limitation can be overcome with MOF surface modifications and the incorporation of hybrid materials into molecule binding sites typically as shown in Fig. 2. This will allow for feasible hybrid MOF processability, band gap engineering, and sensing property tailoring, thus making these MOF materials promising candidates in the construction of electrochemical, optical, and other sensors.
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Fig. 2 Metal organic framework hybrid synthesis via various modfication methods. Reproduced with permission from mdpi.37 |
The thermodynamics and kinetics of MOF structures differ with various metals and ligands used and also differ with each framework design. The relative rate of diffusion of precursors in the solution is fast compared to the formation of metal–organic ligand coordination bonds.38 MOFs are constructed by tailoring inorganic polynuclear metal clusters known as secondary building units (SBUs) and organic linkers via strong bonds that may show a controlled period of homogenous nucleation in complex phase reactions with the chance for good particle size tuning during the growth of these NPs.39,40 SBUs are the key components of MOFs that help to build potentially porous periodic networks by linking multitopic organic ligands and play an important role in the absorption properties of MOFs.41–43 Most MOF NPs are synthesized by any of the following methods, or sometimes in combination: (1) rapid nucleation, (2) nanoreactor confinement, and (3) coordination modulation.44 The various mechanisms involved in the controlled synthesis of MOF NPs are shown in Fig. 3(a–c). The Lamer model of nanoparticle growth was mainly used for understanding the mechanism of MOF NP nucleation and growth as shown in Fig. 3(c). In the Lamer model,44 the process of nucleation and growth takes place in four steps:
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Fig. 3 Schematic diagram of (a) the controlled synthesis of MOF NPs, (b) the post-synthetic surface modification of the MOF, (c) lamer model of four steps of MOF NP formation, and (d) covalent surface modification (top) and coordinative surface modification (bottom) at the SBUs. Reproduced with permission from Wiley.44 |
(1) A swift rise in the number of reactive monomers in solution (stage I).
(2) A uniform nucleation “burst” as the number of reactive monomers surpasses the critical nucleation concentration (Cnuc).
(3) A swift reduction in the number of monomers in the solution, thus stopping the further nucleation process (stage II).
(4) And an increase in crystal growth when the saturation concentration is reached (Csat) (stage III).
To synthesize small, uniform-sized MOF NPs, many nuclei need to be produced through nuclei burst nucleation followed by rapid depletion of precursors to avoid further particle growth. Large MOF NPs are obtained by slow particle nucleation and growth. The standard techniques like X-ray absorption of fine structures,41 high-resolution TEM,42 liquid cell transmission electron microscopy (LCTEM),40 time-resolved static light scattering,43 small- and wide-angle X-ray scattering,38etc. have been performed to find the structural, morphological and porosity characteristics during this nucleation and subsequent MOF fabrication.
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Fig. 4 Typical physic–chemical kinetics of analyte (antibiotic) molecular functional group interaction with surface functionalized MOFs in selective detection and for optical and electrochemical bio/chemical sensor designing. Commonly used transduction methods for sensing such as (A) an electrochemical sensor having a MOF based working electode with subseuqnt analyte responsive redox signal and (B) an optical sensor containing MOF based reagent with a subsequent analyte concentration based spectrocopic signal. Modified from ref. 58 and 59. |
To achieve good sensing properties and methodologies, it might be necessary to apply more than one surface binding mechanisms to enhance the selectivity, adsorptive capability, and transduction mechanism of the sensor.58 This can be achieved by surface functionalization strategies of different types of metal, clusters, or core–shell MOFs through molecule linkers type (typical groups such as hydroxyl, thiol, or amide, biomolecule, aptamers, etc.) which will function as active binding/interaction sites using various physisorption and chemisorption interactions with the analyte as given in Table 3 and Fig. 4.
Type of strategy | Strategy | Typical surfactants/molecules | Ref. |
---|---|---|---|
Replacement | Ligand exchange | Ligands with a chemical group that binds the NP (thiols, amines, phosphines, carboxylic acids), micelle structure, contains a polar head group (hydroxyl) on the other end, etc. | 48 |
Bidentate ligands | |||
Linear and branched polymers | |||
Ligand addition | Similar ligands as used in ligand exchange ones | 49 | |
Noncovalent conjugation | Bilayers | Alkyl carboxylic acids, phospholipids | 50 |
Wrapping | Large-molecular-weight polymers | 51 | |
Encapsulation | Amphiphilic polymers: the hydrophobic groups interact with the surface-bound ligand and hydrophilic groups provide water solubility | 52 | |
Electrostatic conjugation | Highly charged polymers made up of molecular entities with multiple charges | 53 and 54 | |
Metal affinity coordination | NPs with metals on the surface such as Fe2+, Ni2+, Zn2+, or Cu2 + | 53 and 55 | |
Electron donor molecules such as polyhistidine | |||
Host–guest interaction | Coupled moieties like cyclodextrin and adamantyl moieties | 56 | |
Covalent conjugation | Sulfur bridged | Thiol-terminated molecules | 57 |
Click chemistry | Azido-terminated molecules: this allows the crafting of the polymers on the surface of the NPs | 53 | |
Carbodiimide chemistry | Usually for NPs with carboxyl groups on the surface, amine-terminated molecules, amino acids, peptides, and proteins | 53 |
In addition to de novo design, tuning by the post-synthetic modification of the pore interior and/or the inclusion of fluorophores as guest molecules into the pores, such as lanthanide ions, quantum dots (QDs), fluorescence dyes, via coordination or covalent bond formation within the backbone of MOFs is often exploited for optical sensing. The phenomenon of increasing the absorption or emission intensity that represents higher energy absorption and conversion efficiency, i.e., a shift in the emission wavelength across a wider range of wavelengths, offers a good candidate for fluorescence-related MOF applications. With various sensing mechanisms explored using MOFs for antibiotic residue detection, a comprehensive compilation of such recent MOF nanomaterials, their sensing mechanism (optical and electrochemical), linear range, and LOD studied for food and water antibiotic residues is presented in Table 4.
Sensor type | MOF | Sample | Analyte | Mechanism | Linear range | Lod | Reference |
---|---|---|---|---|---|---|---|
a Abbreviations: DOX – doxycycline, TCT – tetracycline, OCT – oxytetracycline, CTC – chlortetracycline, NFZ – nitrofurazone, NFT – nitrofurantoin, MND – metronidazole, RND – ronidazole, OND – ornidazole, and DND – nitroimidazole. | |||||||
Optical based | |||||||
Electrochemiluminescence | Gold incorporated HKUST with a cysteine perylene derivative | Milk | Kanamycin | In the presence of analyte, the catalytic activity of the MOF increases the binding of the aptamer–analyte complex resulting in increased luminescence intensity | 1.0 × 10−13 to 1.0 × 10−8 M | 20.34 pg L−1 | 85 |
Fluorescence | Eu MOF | Water | Metronidazole, dimetridazole | Fluorescence quenching due to PET and FRET mechanisms | — | 13 μg L−1, 13.4 μg L−1 | 86 |
Fluorescence | Eu MOF | Milk, beef | Tetracycline | Inner filter effect and PET | — | 19.1 μg L−1 | 87 |
Ratiometric fluorescence | Zeolitic imidazolate framework-8 incorporated with a gold cluster and green-emitting carbon dots | Milk | Cephalexin | The gold cluster has an emission wavelength of 630 nm and green-emitting carbon dots have an emission of 520 nm when excited at 400 nm. Cephalexin selectively quenches the emission of the gold cluster while the fluorescence of carbon dots remains the same. It can be noted that the ratio of emission (F520/F630) is linearly proportional to the concentration of the analyte | 0.1-6ng L−1 | 0.04 ng L−1 | 88 |
Fluorescence | MIP-coated Zr MOF | Honey, milk | Chloramphenicol | The non-homogeneous adsorption of the analyte on the surface of the MOF enhances the fluorescence emission | 0.16–161.56 μg L−1 | 0.013 μg L−1 | 89 |
Luminescence | Al MOF | Milk | Nitrofurazone, nitrofurantoin, furazolidone | Spectral overlap of absorption spectra of the analyte and excitation spectra of the MOF | — | 105 μg L−1, 200 μg L−1, 131 μg L−1 | 90 |
Fluorescence | Tb MOF | Milk | Tetracycline | Inner filter effect and FRET | 0–244 μM L−1 | 88.5 μg L−1 | 91 |
Fluorescence | Eu MOF | Aqueous media | Ciprofloxacin, ofloxacin | Fluorescence quenching due to PET and dynamic fluorescence quenching mechanisms | — | 0.693 ng L−1, 0.802 ng L−1 | 92 |
Fluorescence | Tb3+ doped Zn MOF | Aqueous media | Nitrofurazone | Inner filter effect and FRET | 0–3.4 μM | 115 μg L−1 | 93 |
Fluorescence | Eu MOF and Tb MOF | Aqueous media | Cefixime, nitrofurazone | At lower concentrations, competitive absorption of the excitation wavelength by the analyte and higher concentration electron transfer between the analyte and MOF | 0–0.05 μM | Eu(cefi) 1.8 mg L−1, Tb(cefi) 1.9 mg L−1, Eu(nitro) 1.8 mg L−1, Tb(nitro) 1.6 mg L−1 | 94 |
Fluorescence | Lanthanide doped Zr and Zn MOF | Milk | Norfloxacin, minocycline | Fluorescence enhancement by the energy transfer from the analyte to the MOF is the detection mechanism in norfloxacin and fluorescence quenching due to the inner filter effect and a possible complex formation in the case of minocycline | 2–200 μM for minocycline, 0.4–20 μM for norfloxacin | 5.6 mg L−1 for minocycline, 19.1 μg L−1 for norfloxacin | 95 |
Fluorescence | Tb MOF | Aqueous media | Nitrofurans, nitroimidazoles, sulfamethoxazole | The nitro group containing antibiotics acts as an electron acceptor and the ligands as the electron donors causing fluorescence quenching, but sulfamethoxazole has a higher LUMO than the ligand and therefore acts as an electron donor and causes fluorescence enhancement. The I544/I400 value increases in the case of nitrofurans as the concentration increases whereas the value decreases in the case of the concentration of nitroimidazoles | — | 98 μg L−1 and 196 μg L−1 respectively for nitrofurantoin and dimetridazole | 96 |
Fluorescence | (Zn-MOF), [Zn2(oba)4(4,4′-bpy)2]n | Aqueous solution | Metronidazole | The absorption spectra of met antibiotic overlap with the fluorescence spectra of Zn-MOF causing fluorescence quenching | 0–400 μM L−1 | 0.81 mg L−1 | 67 |
Fluorescence | {(Cd-MOF) [Cd2(HL)2(bip)2]·H2O}n | Aqueous solution | Chloramphenicol | Fluorescence quenching – the PET process (photoinduced electron transfer) in H3L and antibiotics | 0–10 μM L−1 | 91 mg L−1 | 97 |
Luminescence | Cd-MOF [Cd4(L)4·H2O·EtOH]n | Water | Nitrofurantoin | The overlap between the UV-Vis adsorption band of NFT and the emission of MOF-luminescent quenching | — | 2.4 mg L−1 | 98 |
Fluorescence | [Cd2(HDDB)(bimpy)(NMP)(H2O)] | Water | Nitrofuran/nitroimidazole (1,2-dimethyl-5-nitroimidazole; metronidazole; ronidazole; ornidazole and two nitrofuran antibiotics (nitrofurazone, nitrofurantoin) | Fluorescence quenching by PET (photoinduced electron transfer) and FRET (fluorescence resonance energy transfer) | 0–0.5 mM L−1 | 52 μg L−1 for DND, 80 μg L−1 for MND, 102 μg L−1 for RND, 81 μg L−1 for OND, 136.7 μg L−1 for NFZ and 2.62 mg L−1 for NFT | 65 |
Fluorescence | [Cd2Cl(L)(H2O)]·11H2O | Water | Nitrofuran (nitrofurazone and nitrofurantoin) | Fluorescence quenching by photoinduced electron transfer (PET) | 10−6 to 10−3 M L−1 | 40 μg L−1 for NFZ and 61 μg L−1NFT | 63 |
Colourimetric sensor | Aptamer (Apt)-capped and horseradish peroxidase (HRP)-embedded zeolitic metal azolate framework-7 (MAF-7) (apt/HRP@MAF-7) | Milk and water | Streptomycin | The aptamer interaction with the streptomycin triggers the enzymatic (HRP) catalysis of TMB in the presence of H2O2 | 0.005–6 ng mL−1 | 0.51 pg mL−1 | 74 |
Fluorescence | Ln MOF, Ln = Tb3+ | Water | Oxytetracycline, tetracycline | The absorption spectra of OTC and TCT align with the emission spectra of Ln MOF strips causing fluorescence quenching | 0–0.05 mM L−1 | 0.96 μg L−1, 1.3 μg L−1 for OTC & TCT | 70 |
Fluorescence | Zeolite imidazolate framework-8 (ZIF-8) is anchored on a two-dimensional (2D) amino-functionalized Al-metal organic framework (NH2-MIL-53(Al)) | Milk | Doxycycline, tetracycline, oxytetracycline and chlortetracycline | The overlap of the absorption spectra of TCs with the fluorescence excitation spectrum of ZIF-8/NH2-MIL-53(Al) illustrates that the inner filter effect (IFE) contributes to the fluorescence quenching | 0.004–38.5 mg L−1 for TCT, 0.004–25.7 mg L−1 for DOX, 0.004–32.1 mg L−1 for OTC, 0.005–25.7 mg L−1 for CTC | 1.2 μg L−1 for TCT, DOX, and OTC and 2.2 μg L−1 for CTC | 66 |
Fluorescence | Phosphate and fluorescent dye 6-carboxy-x-rhodamine (ROX) double-labelled aptamers of CMP and the bimetallic organic framework nanomaterial Cu/UiO-66 | Fish | Chloramphenicol | The fluorescence of ROX dye in the absence of CMP antibiotic is quenched by the PET. In the presence of CMP, there is a change in the spatial arrangement of the particle causing the regaining of fluorescence | 0.2–10 nM L−1 | 29 ng L−1 | 68 |
Luminescence | Ln-MOFs {[H3O]-[Ln5(L)4(DMA)2]·4.5H2O}n (Ln = Eu3+ (1) or Tb3+ (2)) | Aqueous medium | Ornidazole | The reduced luminescence intensity is caused by the adsorption of OND in the UV-vis region as well as the collision interaction between MOF structures and free OND that consumes emitted light energy | 490–510 μg L−1 | 2 μg mL−1 | 71 |
Fluorescence | Al MOF@Mo/Zn-MOF heterostructure | Aqueous medium | Doxycycline, tetracycline, oxytetracycline and chlortetracycline | The intense absorption of TCs hinders the excitation energy absorption of the Al-MOF@Mo/Zn-MOF nanoprobe, which results in remarkable FL quenching due to the relevant inner filter effect (IFE) | DOX – 0.001–53.33 μM L−1, TCT, OTC and CTC 0.001–46.67 μM L−1 | 0.25, 0.25, 0.28 and 0.44 μg L−1 for DOX, TCT, OTC and CTC | 64 |
Fluorescence | Europium MOF-Eu-In-BTEC | Fish | Doxycycline | The unique interaction between europium and doxycycline forms a complex which has a dual-channel fluorescence which increases the total emission | 0–6 μM L−1 | 21 μg L−1 | 99 |
Colourimetric | Gold nanoparticle-aptamer combined with iron-MOF (Fe-MIL-53) | Water | Chloramphenicol | The AuNP–aptamer interaction with antibiotic decreases nanozyme (FeO3 MNP) catalysis of TMB in the presence of H2O2 | 50–200 nM L−1 | 8.1 ng mL−1 | 73 |
Fluorescence | Nanoscale luminescent MOF In-sbdc | Milk, fish, pork | Tetracycline | The large overlap between the absorption spectrum of tetracyclines and the emission spectrum of the MOF causes fluorescence quenching | 0–30 μM L−1 | 135 μg L−1 | 100 |
Fluorescence | Dye dopped UiO66 MOF | Milk, honey | Tetracycline | The MOF has a characteristic blue emission (430 nm) due to the dye. But in the presence of TCT, there is red emission (617 nm) from the incorporated Eu3+ ion – TCT complex due to the antenna effect. The blue emission from the dye remains unchanged and hence can be a reference | 0.1–6 μM L−1 | 8.61 μg L−1 | 72 |
Luminescence | Luminescent MOF [Zn8(C5H4N5)4(C14H8O4)6O(C50H44N4)0.5](TMPyPE@bio-MOF | Aqueous medium | Nitrofurazone, nitrofurantoin | The strong adsorption of NFZ and NFT near the excitation wavelength of the MOF suppresses the excitation energy absorption of TMPyPE@bio-MOF-1, causing fluorescence quenching | — | 0.110 μg L−1 for NFZ 0.134 μg L−1 for NFT | 101 |
Luminescence | Zinc-based metal–organic framework of pyromellitic acid (Zn-BTEC) | Fish | Chlortetracycline | The aggregation of the rigid MOF–CTC complex enhances the fluorescence of the media | 0–8 μM L−1 | 14.4 μg L−1 | 102 |
Luminescence | Luminescent metal–organic framework (LMOF) [Zn4O(BCTPE)3] | Water | Nitrofurazone, metronidazole | Excited-state electron transfer from the higher LUMO of H2BCTPE to those of the analyte may occur under photon excitation (PET), resulting in severe fluorescence quenching | — | 0.1 μg L−1, 0.6 μg L−1 | 69 |
Fluorescence | Cu MOF based aptasensor | Milk, fish | Chloramphenicol | The main mechanism is FRET. The aptamer hairpin probe in the sensor along with SYBR green dye, in the absence of CMP, gets adsorbed on the Cu MOF and its fluorescence is quenched. In the presence of CAP, the aptamer forms a ds-DNA with the primer, and its fluorescence is enhanced, and this dsDNA is not adsorbed on the Cu MOF | 0.001–10 ng L−1 | 0.3 pg L−1 | 103 |
Chemiluminescent | Luminescent heterometallic MOF, [NaEu2(TATAB)2(DMF)3]·OH (CTGU-7, H3TATAB = 4,4′,4′′-s-triazine-1,3,5-triyltri-m-aminobenzoic acid, DMF = N,N′-dimethylformamide, CTGU = China Three Gorges University) | Ornidazole | The luminescence quenching is caused by the energy transfer between the compounds | — | 0.18 mg L−1 | 104 | |
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Electrochemical sensors | |||||||
Impedance | Fe MOF | Water | Tetracycline | The antibiotic MOF aptamer complex increases the electron transfer resistance and decreases the current flow | 0.1–105 nM | 48.1 ng L−1 | 105 |
Electrochemical | AuNP/polyethyleneimine functionalized Fe-MOF | Milk | Tobramycin | The f-probe immobilized on the surface of the MOF competes with the tobramycin to produce current | 100 pM to 500 nM | 26.2 ng L−1 | 106 |
Impedance | Co/Ni MOF | Milk | Enrofloxacin | The antibiotic MOF aptamer complex increases the electron transfer resistance and decreases the current flow | 0.001–1 pg mL−1 | 0.354 μg L−1 | 107 |
Immunosensor | Cerium MOF with gold modification | Pork meat | 1-Aminohydratoin | Competitive binding of the analyte and antigen to the antibody embedded in the MOF | 0.001–1000 μg L−1 | 1.35 × 10−7 μg L−1 | 108 |
Impedance | CoNi MOF derivative | Milk, honey | Furazolidone, chloramphenicol | The aptamer–analyte complex reduces the electron transfer at the electrode surface | — | 1.91 μg L−1, 11.31 μg L−1 | 109 |
Impedance | Cu–Tb MOF | Milk | Penicillin | The aptamer–analyte complex reduces the electron transfer at the electrode surface resulting in the electrochemical response | — | 0.84 pg L−1 | 110 |
Electrochemical | Composite of PtPd@Ni–Co hollow nano-boxes (PtPd@Ni–Co HNBs) and poly (diallyldimethylammonium chloride)-functionalized graphene (PDDA-Gr) | Honey | Chloramphenicol | In the presence of CMP, EXO I release a huge amount of trigger DNA (Tr DNA), and this Tr DNA initiates cycle II, which results in the binding of the exposed capture DNA to the signal probes to increase the current flow | 10 fM to 10 nM | 0.32 pg L−1 | 111 |
Impedance | CoNi metallo-covalent organic framework | Milk, chicken egg | Tobramycin | The aptamer analyte complex increases the resistance on the surface of the electrode resulting in reduced electron transfer | — | 0.07 fg L−1 | 112 |
Impedance | Fe/ZIF-8 | Fresh milk | Chloramphenicol and metronidazole | Electrochemical via linear sweep voltammetry | 0.1–100 μM L−1 and 0.5–30 μM L−1 respectively | 10.6 μg L−1 and 28 μg L−16, respectively | 78 |
Impedance | Ag2SiF6-MOF | Aqueous solution | Penicillin | The MOF aptamer antibiotic complex increases the electron transfer resistance of the electrode and decreases the current flow. With the adsorption of penicillin on the surface of the aptamer, MOF NPs, there is a drop in the redox peak of the electrode. The thickening of the electrode with these non-conducting analytes (penicillin) inhibits the electron transfer in the electrode, and hence it detects the varying concentration of penicillin in the solution | 0.001 to 0.5 ng mL−1 | 0.849 pg mL−1 | 79 |
Impedance | Ce/Cu-MOF | Milk | Tobramycin | The negatively charged aptamer- analyte specific immunocomplex blocks the electron and mass transfer to the electrode by acting as a blocking layer | 0.01 pg mL−1 to 10 ng mg L−1 | 2.0 fg mL−1 | 77 |
Impedance | Ce-MOF | Milk | Oxytetracycline | The G quadruplex complex formed between the analyte and aptamer hinders the redox probe access to the electrode | 0.1–0.5 ng mL−1 | 17.4 fg mL−1 | 82 |
Electrochemical | Fe3O4@mC900 | Milk | Oxytetracycline | OTC molecules would interact with aptamers causing less redox probe access to the AE surface and decreasing the electrochemical activity | 0.005 to 1.0 ng mL−1 | 0.027 pg mL−1 | 83 |
Since most sensors use stable MOF structures to detect their corresponding analyte, the collapse of these structures can be ruled out as a reason for the fluorescence quenching. Hence the quenching is mainly due to either one or more of the other reasons mentioned above. The photoinduced electron transfer (PET) is a redox reaction in which excited electrons are transferred from the donor to the acceptor in the presence of light. i.e., one species gets oxidized while the other is reduced. The electron transfer between the metal and the ligand in the HOMO (Highest Occupied Molecular Orbital) and LUMO (Lowest Unoccupied Molecular Orbital) energy levels causes fluorescence/luminescence. Most antibiotic molecules contain furan or benzene rings that can act as electron donors or acceptors respectively. Hence the interaction between the MOF and various antibiotics compounds brings about a quenching of fluorescence/luminescence. The other mechanism is due to the transfer of energy in either direction between light-sensitive molecules i.e., the analyte and the fluorophore. An excited state fluorophore transfers its energy to a ground-state fluorophore through nonradiative dipole–dipole interaction. This interaction is distance dependent and once again exploited by functionalizing MOFs with such fluorophores. The overlap between the absorption spectra of the analyte and the emission spectra of MOF causes quenching, i.e., in both PET and FRET, during the detection of these antibiotic residues, and the emission spectra of MOF are absorbed by the analytes, which decrease the intensity of fluorescence, which can consequently be quantified by using a simple fluorometer. This decrease in the intensity is proportional to the concentration of the analyte. In some sensors, the shift of spectra or enhancement of fluorescence can also occur due to the formation of new complexes.36,62 The inner filter effect can also be a reason for the fluorescence quenching. The ligands absorb energy from a light photon and simultaneously transfer this energy to the transition or lanthanide-type metal ion by the “antenna effect”. The overlapping of the absorption spectra of antibiotics and the excitation spectra of the MOFs blocks the “antenna effect” in transition or lanthanide MOFs due to the filter effect that may act internally in the MOF's sites binding mechanism.
Li et al. confirmed the huge potential of utilizing multi-pyridinium ligands to synthesize functional MOFs with new and better photophysical properties, for switching and sensing applications of nitrofurans antibiotics. The metallic part is cadmium with a 2D fold, while the carboxylate is the electron donor and pyridinium is the electron acceptor which is the cause of the photochromic nature of the used MOF (due to photo-induced electron transfer). The LOD for nitrofurazone and nitrofurantoin was found to be 39.6 and 62 μg L−1 respectively in this work. The broad UV absorption spectra of these materials can be identified as the reason for the fluorescence quenching. There is good overlapping of the light absorption spectra of these nitrofurans with the emission spectra of the MOF thereby inducing an energy transfer from the MOF to antibiotics as well as the extensive overlapping of the absorption spectra of nitrofurans with the excitation spectra of the MOF causing a competitive absorption. Both these overlaps cause fluorescence quenching in 50 s.63
A novel cadmium-based MOF with high pH and water media stability has been synthesized by the solvothermal method and one of the first reported methods to detect multiple analytes such as nitrofuran antibiotics, DNC pesticides, ferric ions, and ascorbic acid by turning off fluorescence due to PET and FRET (Fig. 5(A–C)). There is electron transfer from the conduction band of the MOF to the LUMO of nitrofurans (PET) and an extensive overlap of the absorption spectra of nitrofurans with the emission spectra of the MOF (FRET). The detection limit was found to be 50 μg L−1 for DND, 80 μg L−1 for MND, 100 μg L−1 for RND, 81 μg L−1 for OND, 137 μg L−1 for NFZ, and 262 μg L−1 for NFT.65
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Fig. 5 (A) 2D layer and (B) 3D supramolecular structure of a cadmium-based MOF [Cd2(HDDB)(bimpy)(NMP)(H2O)]·3H2O where (H5DDB = 3,5-di(20,40-dicarboxylphenyl)benzoic acid and bimpy = 3,5-bis(1-imidazolyl)pyridine) sensor for the detection of nitrofurans, and (C) fluorescence emission linear spectra of the analyte with the cadmium MOF. Modified and reproduced with permission from the Royal Society of Chemistry.64 [Zn4O(BCTPE)3] MOF where (D) is the structure of the BCTPE2− ligand, (E) is the structure of the Zn4O(CO2)6 node, and (F) is the 2-fold crystal structure of the entire MOF. (G) Fluorescence titration of nitrofurazone antibiotic with the MOF. Modified and reproduced with permission from the Royal Society of Chemistry.69 |
A dual MOF with a 3D architecture using aluminium and zinc exhibited brilliant performance and specificity for tetracycline sensing with the inner filter effect and photo-induced electron transfer as the main sensing mechanisms with a wide range of response, ultra-low LOD, and superior selectivity against common interfering compounds such as other antibiotics, amino acids, sugars, some metal ions, and compounds with –NH2 functional groups. All major 4 tetracyclines can be detected using this sensor with LODs of 0.24 μg L−1 for doxycycline, 0.25 μg L−1 for tetracycline, 0.28 μg L−1 for oxytetracycline and 0.44 μg L−1 for chlortetracycline. The hydrogen bonding between the OH/COOH of tetracycline with the NH2 group in this MOF as well as the electron transfer from the MOF to tetracyclines (via PET) resulted in effective fluorescence quenching.64
A fluorescence turn-on sensor was developed by utilizing the strong coordination between the phosphate backbone of an aptamer and zirconium ions in a bimetallic coordination bonding MOF of UiO-66 and copper. It is a selective and sensitive sensor with a low LOD of 29 ng L−1 for the detection of chloramphenicol in fish. In the absence of CMP, the fluorescence of ROX fluorophore is quenched by the MOF as it comes in close contact with the surface when the aptamer is adsorbed on the surface of the MOF through PET. But in the presence of CMP, this close contact is avoided due to the formation of a CMP–aptamer complex with a special spatial structure resulting in fluorescence of ROX detected. The quantity of CMP is proportional to the intensity of fluorescence of ROX.68 A luminescent MOF of zinc and dicarboxyl-substituted tetraphenylethene (TPE) was reported by Liu et al., for the detection of nitrogen-containing antibiotics such as nitrofurazone and metronidazole with a LOD of 0.1 and 0.6 μg mL−1 respectively. The luminescence quenching was attributed to photoinduced electron transfer. The excited-state electron from the highest LUMO of H2BCTPE gets transferred to those of the analyte because of photoexcitation (Fig. 5(D–G)).69
Chongliang et al. reported the development of lanthanide-based MOF (terbium & salicylic acid) test strips which were highly sensitive and the response to the analyte was not hindered by any other components present and the strips were cheap, can be reused at least 6 times, were portable and rapid with a testing time of only 1 minute and were easy to use. The detection was based on the antenna effect i.e. the absorption spectra of tetracycline and oxytetracycline (360 nm) overlap with the excitation wavelength of the terbium MOF (361 nm) which resulted in competitive absorption and thereby fluorescence quenching. The MOF was based on the inner filter effect and the LOD was found to be 0.93 μg L−1 and 1.37 μg L−1 for tetracycline and oxytetracycline respectively.70
A bimetallic lanthanide (europium and terbium) MOF was transformed into a luminescent sensor to detect antibiotics for practical uses such as its detection in water. The luminescent study showed that the membranes made from these materials could work as a self-calibrating luminescent probe for various antibiotics in a specific concentration range and it could be used as an inexpensive and convenient prototype sensor to distinctively determine different antibiotics, which enhances its potential practical applications. The limit of detection was found to be 2 μg mL−1 and the fluorescence quenching is caused by the overlapping of excitation spectra of the MOF and the absorption spectra of ornidazole as well as the collision between the free ornidazole and MOF resulting in energy transfer.71
Jia et al. used a real-time MOF sensor with a dye that induces UiO66 encapsulated in SiO2 and Eu3+ for the detection of tetracycline in honey and milk. The LOD was found to be 8.61 μg L−1 and the linear range was 0.1–6 μM. The MOF has a blue emission when excited from the dye incorporated. In the presence of tetracycline, a complex is formed between the Eu metal and TC which gave a red emission (617 nm) via the ‘antenna effect’ (Fig. 6(A–C)). This nanoprobe discussed had a LOD of 48.1 μg L−1 during onsite detection.72
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Fig. 6 (A) Fabrication of the Dye@UiO-66-@SiO2–NH2-Cit-Eu lanthanide MOF and its sensing of tetracycline, (B) fluorescence spectra and the fluorescence images of the MOF with concentrations of tetracycline antibiotic and (C) the red and blue chromaticity analysis of the fluorescence emission of the MOF with tetracycline calculated using a smartphone. Modified and reproduced with permission from mdpi.72 |
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Fig. 7 Colorimetric MOF sensor for chloramphenicol: (A) the schematic design depicting the binding and detection of chloramphenicol based on the antibiotic-aptamer/AuNP-aptamer interaction and enzyme mimetic activity of iron-based MOFs. (B) UV-vis absorbance spectra of the MOF in the presence of various concentrations of CMP. Adapted and reproduced with permission from Elsevier.73 |
The work by Wang et al. reported a MOF aptamer colourimetric sensor that was sensitive and selective with excellent accuracy for streptomycin with a streptomycin-specific aptamer which can be replicated for other antibiotics by changing the aptamer sequence for onsite detection of antibiotics in milk. The sensor contains a zeolitic metal azolate framework-7 (MAF-7) embedded with an antibiotic-specific aptamer and horseradish peroxidase (HRP) enzyme. The enzyme catalytic activity is increased 4 fold in the HRP-MOF composite. This composite oxidizes TMB in the presence of H2O2. But in the presence of streptomycin, the aptamer antibiotic complex forms a layer over the HRP-MOF composite, which results in a decrease in catalytic activity. The decrease in intensity is proportional to the concentration of the antibiotic residue. The LOD of this sensor was found to be 0.51 pg L−1, which is less than that of most conventional methods of detection.74
One of the major issues is the comparatively poor water stability of pristine MOFs since the metal–ligand coordination bonds can be readily cleaved by water molecules and hence often is a limiting factor for electrochemical sensing. From the electroanalytical point of view, MOF functionality is understood through its chemical stability in the targeted electrolytes and the stability of the MOF structures after the completed electroanalytical process. Apart from the MOF thin film deposited on the working electrode surface, metal-coordinated organic linker nodes, supporting electrolytes with varying ionic concentrations, and the buffer solutions used are some of the required parameters in electrochemical sensing operations.
The electrochemical sensing performances of redox-active MOFs can be exhibited by promising redox-active moieties and molecular sites that rely on redox hopping to transport electrons during the electroanalytical processes. Redox hopping is generally combined with both electron transport and the diffusion of active ionic species within the frameworks. However, in certain applications, the characteristic of MOFs with larger pore sizes is not always desirable, because it may decrease the density of active sites, and the active site's electron transport rate and will thus start to limit the overall electrochemical process. But, to achieve a better electroanalytical performance, improving the charge transport within the MOF materials that possess sufficiently large pore sizes for the diffusion of counter ions plays an important role in attaining the targeted analyte detection by this method.
Conducting-type sensors are rarely synthesized using MOFs, and the reason is the presence of bulk organic linkers that are essentially insulators. But recently some attempts have been made to use electrochemical impedance for the detection of antibiotic residues.78 An aptamer-based electrochemical MOF sensor for enrofloxacin detection was discussed by Song et al. where the sensor is based on a semiconducting bimetallic Co/Ni MOF with 2,3,6,7,10,11-hexaiminotriphenylene as the ligand. The LOD of this sensor was found to be as low as 0.2 fg mL−1. The sensing was determined using impedance electrochemistry where sinusoidal alternating current is passed through the solution to measure the total resistance.81 He et al. developed an aptamer-based electrochemical sensor having an Ag MOF for the ultrasensitive detection of penicillin with a LOD of 0.849 pg mL−1 in raw milk. The MOF aptamer antibiotic complex increases the electron transfer resistance of the electrode and decreases the current flow. With the adsorption of penicillin on the surface of aptamer-MOF NPs, there is a drop in the redox peak of the electrode. The thickening of the electrode with these non-conducting analytes (penicillin) inhibits the electron transfer in the electrode, and hence it detects the varying concentration of penicillin in the solution.79
The analysis of chloramphenicol and metronidazole by using an electrochemical sensor via linear sweep voltammetry using an iron, nitrogen co-doped nanoporous carbon–metal–organic framework (type Fe/ZIF-8) on a glassy carbon electrode was also recently discussed by Baikeli et al., in real samples. The complex is simple with a large surface area, mesopores, and particle size. There are three reasons for the electrochemical activity of the Fe/NC framework. They have a large electroactive surface area, fine conductivity of the Fe/NC framework, and the catalysis of Fe atoms to chloramphenicol and metronidazole. The reported LOD was 10.6 μg L−1 and 28.6 μg L−1 for chloramphenicol and metronidazole respectively.78 Wang et al. also developed a bimetallic cerium/copper aptamer-based MOF for the ultra-sensitive detection of tobramycin in milk which had a LOD of 2.0 fg mL−1. The MOF-modified aptamer electrode is used as the working electrode, a platinum wire as the counter electrode, Ag/AgCl as the reference electrode, and a 1:
1 mixture of K3[Fe(CN)6]/K4[Fe(CN)6] as a redox probe. The aptamer–analyte complex reduces the diffusion of Fe(CN)63−/4− to the electrode surface resulting in a reduced current flow.77 A hybrid nanocomposite aptasensor of a porous organic framework and cerium-MOF for the detection of oxytetracycline in milk was described by Zhou et al. as seen in Fig. 8(A and B). The LOD for this sensor was found to be 17.4 fg mL−1 and the linear range to be 0.1–0.5 ng mL−1. Melamine and cyanuric acid monomers are the precursors used in the synthesis of this organic framework. There is a strong interaction between the aptamer strands and the nanocomposite, which helps in the immobilization of aptamers and subsequent analyte absorption. An A-G DNA quadruplex complex is formed between the oxytetracycline and the aptasensor due to the amide bond, which decreases the redox signal of the electrode because of steric hindrance by the formed complex. The electrochemical changes were measured using electrochemical impedance spectroscopy.82 Song et al. described an oxytetracycline sensor with a LOD of 0.027 pg mL−1 and a linear range between 0.005 and 1.0 ng mL−1. The gold electrode is used as a working electrode, Ag/AgCl as a reference electrode, and a platinum slide as a counter electrode. An Fe3O4 mesoporous carbon was coated on the working electrode along with an oxytetracycline-specific aptamer. The oxytetracycline forms a G-quadruplex complex with the aptamer, which results in low redox probe access to the working electrode which decreases the electrochemical activity.83
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Fig. 8 (A) Schematic diagram of the fabrication procedure of the Ce-MOF@MCA-based aptasensor for detecting oxytetracycline (OTC). (B) Nyquist plots for the detection of different concentrations of OTC using the Ce-MOF@MCA500-based aptasensor. Modified and reproduced with permission from Elsevier.82 |
Recent advancements in MOF sensors for antibiotic detection include a solvothermally synthesized 3D europium MOF with wide pH stability (3–12) as discussed by Wang et al., which can rapidly detect metronidazole and dimetridazole with recyclability and a LOD of 13 μg L−1 (metronidazole) and 13.4 μg L−1 (dimetridazole) in lake water (Fig. 9(C and D)).86 The mechanism was found to be due to the transfer of electrons from the conduction band of the MOF to the LUMO of analytes (via PET) and overlapping of the UV spectra of the analyte and MOF, which results in fluorescence quenching.86 This MOF can be further modified to analyze antibiotic residues in food, feed, and water.
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Fig. 9 (A) Double-stranded helical structure of the Tb-MOF along the a-axis with right and left views. (B) The related luminescence intensity of Tb-MOF with different antibiotics. Modified and reproduced with permission from the American Chemical Society.96 (C) [Eu2(dtztp)(OH)2(DMF)(H2O)2.5]·2H2O MOF 3D framework and (D) fluorescence bands of the above-mentioned MOF upon addition of metronidazole and dimetridazole antibiotics respectively. Modified and reproduced with permission from Elsevier.86 (E) 2D network structure of Eu-MOF, and (F) and (G) the fluorescence spectra comparison and colour change when Eu-MOF is added with ciprofloxacin and ofloxacin antibiotics respectively. Modified and reproduced with permission from the American Chemical Society.92 |
A new europium-based MOF was described by Xiao et al., for the selective detection of ciprofloxacin and ofloxacin which had a LOD of 0.693 ng L−1 and 0.802 ng L−1 respectively (Fig. 9(E– G)).92 The fluorescence quenching is caused by PET and the dynamic quenching mechanism. At low concentrations, there is no formation of a complex but at higher concentrations, there is a complex formation. There is also electron transfer from the LUMO of the analyte and the LUMO of the ligand in the Eu MOF (via PET). This sensor is a very powerful tool for the detection of the above antibiotics as it helps in rapid detection, and easy identification with the naked eye, and has a low LOD. The red emission of MOF changes to blue in the presence of ciprofloxacin and changes to green in the presence of ofloxacin.86 A ratiometric sensor comprising zeolitic imidazolate framework-8 incorporated with gold clusters and green-emitting carbon dots with dual emissions for the detection of cephalexin in milk is developed. The gold cluster has an emission wavelength of 630 nm and green-emitting carbon dots have an emission of 520 nm when excited at 400 nm. The cephalexin selectively quenches the emission of the gold cluster while the fluorescence of carbon dots remains the same. It can be noted that the ratio of emission (F520/F630) is linearly proportional to the concentration of the analyte. This linear relationship is seen in the range of 0.1–6 ng L−1 and the detection limit was found to be 0.04 ng L−1.88 The europium MOF was developed for the detection of tetracycline in milk and beef with a LOD of 19.1 μg L−1. This MOF has red fluorescence at 617 nm when excited at 260 nm. In the presence of tetracycline, the fluorescence is quenched and can be distinguished with the naked eye. The inner filter effect (overlapping of excitation spectra of the MOF and absorption spectra of the analyte) and PET (transfer of an electron from the MOF to the analyte) were considered to be the reason for quenching. Furthermore, importantly a test strip using this MOF was made with deposition on the MOF on a paper surface. This can be used for the onsite detection of tetracycline (Fig. 10(1)).87
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Fig. 10 (1) Eu MOF-based portable test strip for rapid and visual detection of tetracycline based on a simple spectrofluorometer. Reproduced with permission from Elsevier.87 (2) Detection of nitrofurantoin metabolite 1-aminohydantoin using Ce-MOF@Au by the electrochemical immunosensing technique. Reproduced with permission from Elsevier.108 |
Zhang et al. developed an aptasensor for the detection of tobramycin using electrochemically deposited gold nanoparticles coordinated with polyethyleneimine functionalized Fe-MOF. The LOD was found to be 56 pM and the linear range to be 100 pM to 500 nM. An f-probe (complementary DNA strand to tobramycin aptamer) was immobilized on the surface of the MOF along with the aptamer. In the absence of TOB, the f-probe and aptamer form a complete DNA structure so that very little current flows. But, in the presence of TOB, the f probe remains unhybridized and a very high current flow is observed. This current flow is proportional to the concentration of TOB.106 A heterometallic MOF of copper and terbium with DMF as a ligand was employed for the detection of penicillin in milk. This electrochemical aptasensor has a LOD of 0.84 pg mL−1, which can be considered very low and can be considered highly sensitive. The aptamer–analyte complex reduces the electron transfer on the surface of the electrode by increasing the resistance. This reduced current flow is proportional to the concentration of penicillin. The recovery range of penicillin in milk by the MOF was between 100.3 and 113.4%. This indicates that this sensor can accurately determine penicillin in raw milk.110 An electrochemical aptasensor with a composite of PtPd@Ni–Co hollow nano-boxes (PtPd@Ni–Co HNBs) and poly (diallyldimethylammonium chloride)-functionalized graphene (PDDA-Gr) was developed for ultrasensitive detection of chloramphenicol (CMP) and was tested in honey. In the presence of CMP, EXO I releases a huge amount of trigger DNA (Tr DNA), and this Tr DNA initiates cycle II, which results in the binding of the exposed capture DNA to the signal probes to increase the current flow. This aptasensor has a wide linear range (10 fM to 10 nM) and a detection limit of 0.32 pg L−1.111
A simple, rapid, selective, sensitive, and low-cost aptasensor for the detection of tetracycline using an Fe MOF(NH2-MIL-101(Fe)/CNF@AuNPs) was synthesized using the combination of 4 different methods such as hydrothermal, electrospinning, pyrolysis, and electrodeposition resulting in increased sensitivity to the analyte. In the presence of TC, the aptamer–analyte complex on the surface of the electrode reduces the electron transfer on the surface of the electrode due to impedance resulting in reduced current. The LOD of this sensor was found to be 48.1 ng L−1 and under optimum conditions, there is a linear relationship between impedance and concentration (0.1–105 nM).105
An electrochemiluminescent aptasensor for the detection of kanamycin was discussed by Wen et al., with gold-incorporated HKUST(Au@HKUST) with a cysteine perylene derivative (PTC-Cys)/peroxydisulfate (S2O82−) with an ultra-low LOD of 20.34 pg L−1. The MOF part of the sensor acts as a catalyst for the electrochemical reduction of S2O82− to a sulfate radical anion. In the presence of the analyte, the complex of analyte–aptamer enhances the electrochemiluminescence as it pulls the aptamer from the surface. The cysteine perylene used here is a luminophore. This is a highly selective sensitive stable sensor and can be used for monitoring food safety and was demonstrated using milk with a recovery rate of 96.5–101.72%.85
The first-ever attempt at simultaneous detection of furazolidone and chloramphenicol using a modified glassy carbon electrode using bimetallic Co/Ni MOF-derived hollow NiCo2O4 in milk and honey was discussed by Xia Niu and the team. The LOD of FZD was found to be 1.91 μg L−1 and 11.31 μg L−1 for CMP. Mechanism studies show that there is a reduction of both analytes on the surface of the electrode via a four-electron four proton process causing an increase in current flow. The experiments on milk and honey give appreciable results and hence it can be used for monitoring the quality of these products.109 Amiripour et al. presented a new idea of incorporating a nanostructured molecular imprinted polymer (MIP) coated luminescent zirconium MOF with a CMP template for the detection of chloramphenicol in milk and honey. The sensor has many recognition sites and hence selective absorption of CMP on the surface of the MOF with the help of a MIP. Acceptable recoveries were obtained from the real samples with a LOD of 0.013 μg L−1 and a linear range of 0.16–161.56 μg L−1. In the presence of CMP, there is non-homogenous adsorption of CMP on the MOF surface, and this interaction enhances the fluorescence of the MOF, i.e. in the presence of CMP, there is a turn on of the fluorescence of the MOF.88
MOF sensors for antibiotic residue detection so far vastly employed luminescence/fluorescence quenching mechanisms since most MOFs are fluorescent or luminescent and this ability is used to detect various antibiotic residues in numerous food samples. Developing MOFs by utilizing aggregation-induced emission luminous (AIEgens) as organic linkers (AIE-MOFs) is another aspect that could in the future be used to develop AIEgens activity-based sensors that show simple and effective ‘‘turn-on’’ responses for analytes with the limited label or label-free approach for antibiotic detection.114,115 As seen, these novel nanomaterials have a very low LOD and excellent selectivity mainly because of their nanoscale porosity which offers internal high sensibility, the molecular sieve effect of the uniformly distributed cavities, and the exposed ligands present contribute towards selective recognition.115 In this way, MOFs are tunable and specifically designed for selective sensing purposes. But certain limitations persist with these materials considering that MOFs are difficult to synthesize in a controlled fashion and the procurement of various framework components can be expensive. The size, shape, and porosity all are critical factors that enable a MOF material to sense an analyte and it is still difficult to precisely control these parameters during synthesis. This provides the opportunity to explore many more new synthesis routes that would allow the facile reproduction of these MOFs. For example, most of the MOF's synthesis involves conventional solvothermal methods, which involve solvent-based reactions of metal ions with organic linkers and subsequent crystallization in a closed vessel where high temperature and pressure (above the boiling point of a solvent) facilitate self-assembly and crystal growth.116 Alternative to this is mechano-chemical methods which have gained new traction lately as a green and cost-effective route of MOF synthesis. This method involves high-speed grinding of metal and organic ligands in a ball mill, which results in a shorter reaction time, less energy consumption, high yield of MOF material, and easy scale up as well.116 The recent advance in this method includes the use of a small quantity of solution, which helps in the movement of metal ions and ligands that subsequently improves the reaction. Most solvents used in the conventional synthesis route are hazardous. Hence this method which particularly is solvent-free or uses a very small quantity of solvent is advantageous. Moreover, the use of ionic and supercritical liquids in this method is highly efficient in dissolving organic and inorganic materials and helps in the synthesis of new architectures in MOFs. Supercritical fluids help in structure direction and modification as well.117 Flow synthesis is another method recently developed for the synthesis of MOFs. The most important advantage of this method is the ability to control the size by in situ UV absorption spectroscopy. The characterization and size monitoring of MOFs in fluid media is often very difficult to achieve. Li et al. introduced an integrated system of a flow synthesis system produced by femtosecond laser micromachining and UV spectroscopy where the size of the crystal ranged from 200–1025 nm.118 All these synthesis advancements can also be extended toward developing MOFs specifically for antibiotic residue detection.
Due to the insulating properties of most of the organic ligands, the electrochemical properties of MOFs are also poor, and not much study has been conducted in these areas where novel electrochemical transduction systems have been explored. Few latest studies are being conducted to improve the conductivity of MOFs with nanosheet and nanowire architectures. Realistic electrochemical-based sensors can be attained by improving the conductivity and design of redox-active MOF materials by introducing non-native conductive functional materials such as metal nanoparticles, carbon nanostructures, polymers, and biomolecules into MOF porous structures in a synergistic manner to improve the overall performance of the resulting MOF nanocomposite.119 For example, Chen et al. reported for the first time the integration of Pt nanocrystals (known for catalytic oxidation of alcohol and the photothermal effect in surface plasmon resonance) into a porphyrinic MOF (known to be an effective photosensitizer for 1O2 generation) producing a MOF nanocomposite Pt/PCN-224(Zn) that showed such excellent and selectively enhanced catalytic activity towards photooxidation of aldehydes in aromatic alcohol oxidation by 1 atom O2 at ambient temperature.120 Here, PCN-224(Zn) exhibited the greatest ability for O2 activation and 1O2 production because of strong diamagnetism from Zn2+ compared to other residing metals in the porphyrin MOF, whereas the electronic state of Pt NPs can be tuned to light-intensity for O2 activation based on competition between its Schottky junction and plasmonic effect. Similarly, Wang et al. had developed a Cu@HUKAST-1 MOF nanocomposite via in situ etching and the resulting composite had enhanced photothermal catalytic activity for a one-pot cascade reaction.121 Such strategic examples can be realized to develop functional MOF based electrochemical electrodes when combined with multivalent ligands and metal nodes to enhance their redox activity, controlled immobilization methods for stable signal amplification and the introduction of many functional groups for water stability.119 Hence, this offers many more opportunities to explore new methods specifically for antibiotic residue detection.
Another major concern is water stability and pH stability of MOFs. The MOFs with metal and nitrogen-containing ligands are more alkaline stable whereas the metal–oxygen bond is acid-stable.119 The instability of MOFs in water can be addressed by using hydrophobic functional groups or making the coordinate bonds between the metal node and ligand more functionally robust. Conventional synthesis methods with large particle sizes have always been one of the biggest disadvantages in the development of MOFs with unique properties. A new method of synthesis was described by Guoyu Wei and team which was termed the microplasmic electrochemical strategy.124 In this method, a modified electrochemical method is employed for the synthesis of a very common MOF, HKUST-1, in a rapid and controlled synthesis manner. A 10 mA current was discharged for 15 min using a microplasma cathode in a precursor solution of cupric nitrate and 1,3,5-benzene tricarboxylic acid dissolved in DMF in a H-type reaction equipment. The mesoporous diameter of the obtained MOF was calculated using the Barrett–Joyner–Halenda method and was found to be 1.8 nm. The concentration, current discharge, etc. have a proportional relation to the amount of MOF synthesized.124 These latest studies such as the microplasma electrochemistry strategy and mechano-chemical methods are promising steps toward synthesizing stable and highly efficient MOFs. Some of them also take leaps towards the green synthesis of MOFs so that less hazardous chemicals are used. It is also worth noting that most sensors have not ventured into testing in real-life samples. The detection in most cases is based on the overlapping of the emission spectra and the absorption spectra of the antibiotic i.e., the photons emitted by the MOF during emission are directly absorbed by the analyte and hence there is fluorescence quenching.122 But in some rare cases, the excitation wavelength of the MOF and the absorption wavelength of antibiotics overlap with each other, thereby causing competitive absorption. This can lead to decreased excitation and therefore less emission. The scenario with a higher concentration of antibiotics is different. Researchers suggest that at a high concentration of antibiotics, there may be the formation of a complex of antibiotics and the MOF with a chemical bond, but the structure and nature of these complexes are yet to be studied. The mechanism of fluorescence quenching caused by this complex is also unknown.
Most electrochemical sensors utilize the resistance created by the presence of antibiotic–aptamer complexes as the most prominent mechanism. The MOF in the absence of an analyte conducts electricity but has an innate resistance. When antibiotic molecules are present in the sample, the total resistance of the solution increases compared to the pristine MOF reagent due to the redox reaction which may be observed as a reduction in the working electrode current flow. Hence, this new resistance/impedance also decreases the current flow through the solution. This change in current flow is measured and used for the quantification of antibiotic residues. Although MOFs identify target analytes through their interactions via hydrogen bonding, π–π interactions, open metal sites, and van der Waals interactions,119 more studies should be carried out to understand the complexity of its mechanism of sensing and the nature and stability of MOF-antibiotic complexes. Along with this, the complexity of food matrices and difficult clean-up procedures contribute to the reason why these materials were not used to perform real-life sample analysis in many studies. Very few of the reported MOF sensors have made it into real-life testing, and most of them have focused only on milk samples which can be considered a common food product. More researchers must focus on developing sensors for other food products such as meat, seafood, eggs, offals, vegetables, and edible crops along with many processed products as well.
Ideally, a good sensor, in this case, would be the use of a MOF nanomaterial (or nanocomposite) that could serve as a platform for multiplexed antibiotic residue detection and quantification in a single sample. Research should also focus on developing a MOF nanocomposite-based surface-enhanced Raman spectroscopic (SERS) method for antibiotic residue detection in food since Raman spectroscopy is capable of even label-free, single-target molecule fingerprinting. A recent study has used a magnetic MOF nanocomposite such as Au/Fe3O4/MIL-101(Cr) as a SERS substrate for antibiotic residue detection in environmental samples.125 Such studies can also be extended towards food samples for rapid molecular-level detection. Although several attempts have been successfully made as mentioned in the previous section, further efforts could also be conceptualized with MOF nanomaterial integrated lab-on-chip technology such as integrated molecular spectroscopy, array-type sensors, and optical fiber-based sensors for a feasible simultaneous, individual discrimination of each antibiotic residue and its quantification for real-time, on-site, routine food sample analysis.60,123
CMP | Chloramphenicol |
CTC | Chlortetracycline |
DNA | Deoxyribose nucleic acid |
DOX | Doxycycline |
ELISA | Enzyme-linked immune sorbent assay |
FL | Fluorescence |
FRET | Fluorescence energy transfer |
FSSAI | Food safety and standard authority of India |
GI | Gastrointestinal tract |
HOMO | Higher occupied molecular orbital |
HPLC | High-performance liquid chromatography |
HRP | Horse radish peroxide |
IFE | Inner filter effect |
LC-MS | Liquid chromatography-mass spectroscopy |
LCTEM | Liquid cell tandem electron microscopy |
LOD | Limit of detection |
LU | Luminescence |
LUMO | Lower unoccupied molecular orbital |
MND | Metronidazole |
MOF | Metal–organic framework |
MRL | Maximum residue limit |
NFT | Nitrofurantoin |
NFZ | Nitrofurazone |
NPs | Nanoparticles |
OND | Ornidazole |
OTC | Oxytetracycline |
PET | Photo-electron transfer |
PSM | Post-synthetic modification |
RET | Resonance energy transfer |
RND | Ronidazole |
ROX | 6-Carboxy-x-rhodamine |
TC | Tetracyclines |
TCT | Tetracycline |
TEM | Tandem electron microscopy |
TMB | 3,3′,5,5′-Tetramethylbenidine |
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