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New Analytical Methods
A Sensitive and Simple Competitive Biomimetic Nanozyme-Linked Immunosorbent Assay for Colorimetric and SERS Sensing of Triazophos Mengmeng Yan, Ge Chen, Yongxin She, Jun Ma, Sihui Hong, Yong Shao, A. M. Abd El-Aty, Miao Wang, Shanshan Wang, and Jing Wang J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.9b03401 • Publication Date (Web): 05 Aug 2019 Downloaded from pubs.acs.org on August 6, 2019
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A Sensitive and Simple Competitive Biomimetic Nanozyme-Linked
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Immunosorbent Assay for Colorimetric and SERS Sensing of Triazophos
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Mengmeng Yan1, Ge Chen1, Yongxin She1*, Jun Ma1, Sihui Hong1, Yong Shao1, A. M.
4
Abd EI-Aty2, 3, Miao Wang1, Shanshan Wang1, Jing Wang1**
5
1 Institute
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Academy of Agricultural Sciences, Beijing 100081, P.R China
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2 Department
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12211-Giza, Egypt
9
3Department
10
of Quality Standards & Testing Technology for Agro-Products, Chinese
of Pharmacology, Faculty of Veterinary Medicine, Cairo University,
of Medical Pharmacology, Medical Faculty, Ataturk University, 25240-
Erzurum, Turkey
11 12 13 14 15 16 17
*(Y.
S.) Tel: +86 10 82106513; Fax: +86 10 82106567. E-mail:
[email protected] 18
**(J.
W.) Tel: +86 10 82106568; Fax: +86 10 82106568. E-mail:
[email protected] 19 20 21 22 23 24 25 1
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ABSTRACT
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Biomimetic enzyme-linked immunosorbent assay (BELISA) is widely used for
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detection of small molecule compounds due to low cost and reagent stability of
29
molecularly imprinted polymers (MIPs). However, enzymes labels used in BELISA
30
still suffer some drawbacks such as high production cost and limited stability. To
31
overcome the drawbacks, a biomimetic nanozyme-linked immunosorbent assay
32
(BNLISA) based on MIPs and nanozyme labels was first proposed. For nanozyme
33
labels, Pt NPs (platinum nanoparticles) acted as peroxidase by catalysing the oxidation
34
of colourless 3,3′,5,5′-tetramethylbenzidine (TMB) into an ideal SERS marker—blue
35
TMB2+ and BSA-hapten (bovine serum albumin-hapten) showed superior selectivity
36
when competing with targets for binding sites on MIPs, which named Pt@BSA-hapten
37
probe. The BNLISA method was employed to detect triazophos with a limit of detection
38
(LOD) of 1 ng·mL-1 via colorimetric and SERS methods. Replacing traditional
39
enzymes with nanozymes for combination with MIPs may bring about a new prospect
40
for other compound analyses.
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KEYWORDS: Molecular imprinted polymer; BNLISA; Triazophos; Nanozyme;
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Horseradish peroxidase
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INTRODUCTION
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Owing to the favourable properties such as mechanical, thermal and chemical
45
stability, ease of preparation, and low cost 1, 2, molecularly imprinted polymers (MIPs)
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have earned a reputation as ‘‘plastic antibodies’’. Thus, MIPs are used in a wide range
47
of applications encompassing the fields of separation, chromatography, immunoassays, 2
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antibody mimics, (bio)sensors
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is considered the gold standard for highly sensitive qualitative and quantitative
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detection of analytes within various samples 7. With the application of MIPs as bionic
51
antibodies for small molecule detection via the ELISA method, biomimetic ELISA
52
(BELISA) came into being. For instance, Piletsky et al. developed MIP microplate
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wells specific for epinephrine, and the affinity of the polymers was determined by
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BELISA using a conjugate of horseradish peroxidase and norepinephrine (HRP-N)8. In
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2003, Chianella et al. synthesized vancomycin MIPs and achieved the detection of
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vancomycin by BELISA in competitive binding experiments with an HRP–vancomycin
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conjugate 9. In the same year, Tang et al. also detected metolcarb by direct competitive
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BELISA10. Subsequently, many other studies on BELISA were also reported11-15.
3-6.
The enzyme-linked immunosorbent assay (ELISA)
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MIPs possess favourable properties such as mechanical, thermal and chemical
60
stability, ease of preparation, and low cost. However, HRP labels in BELISA method
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could not adapt to a wide range of temperature and pH conditions. Therefore, the
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combination between HRP and MIPs may limit the applicability of MIPs as a
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biomimetic antibody. Recently, the demand for nanozymes has increased due to their
64
advantages, such as simple preparation, high temperature and pH stability, easy surface
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modification and low cost16-18.
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Consequently, we proposed a biomimetic nanozyme-linked immunosorbent assay
67
(BNLISA) integrating MIPs with nanozymes for detecting triazophos to broaden
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applicability of MIPs as a biomimetic antibody. Pt NPs were opted as the nanozyme in
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our project owing to their advantages of enzyme-like peroxidase activity, simple 3
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synthesis, good tunability, easy storage and easy surface modification by using DNA
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and protein19-23. The structural analogues of triazophos (hapten) must be introduced to
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form a competitive relationship with triazophos when they distinguished the binding
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sites on MIPs. BSA was used as a “bridge” linker due to its abundant functional groups
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such as amino, carboxyl, thiol and disulfide that could be reacted with other molecules
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and nanoparticles24, 25., Hence, the nanozyme label was fabricated by two steps. Firstly,
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BSA-hapten conjugates were synthesized by carbodiimide method between amino
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groups from BSA and carboxyl groups from hapten compounds. And then the BSA-
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hapten conjugates were mixed with Pt NPs colloid solution for forming Pt@BSA-
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hapten probes. Therefore, the as-obtained Pt@BSA-hapten was not only employed as
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competitive probe to recognize the MIPs binding site, but also played a crucial role in
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acting as signal probe due to the presence of massive Pt NPs.
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To obtain biomimetic 96-well MIPs array plate by directly synthesizing molecular
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imprinted films onto the plate requiring massive raw materials. Meanwhile, the films
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were easy to break off resulting in inhomogeneous films from well to well when
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templates were removed by ultrasonic method12. To avoid these matters, uniform MIP
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microspheres were got firstly by precipitation polymerization and then they were
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immobilized onto 96-well array plate by the “grafting to” method with the assistance
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of ionic liquid (IL) as a binder26, 27.
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To demonstrate the universal detection capability of the BNLISA method,
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triazophos was selected as the model target. Triazophos is a broad-spectrum
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organophosphate pesticide that has been widely used in agriculture to control insect 4
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pests16, 28. However, owing to its relatively high stability and long half-life, it presents
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potential risks to human health and the environment29, 30.
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In this proposal, colorimetric and surface enhanced surface-enhanced Raman
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scattering (SERS) were selected to evaluate the practicality of the BNLISA method
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thanks to the catalysate TMB2+. SERS is an advanced Raman technique, and was
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observed by Fleischmann and Van Duyne group in the 1970s. SERS is highly specific
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and sensitive for detection molecules due to characteristic fingerprints of SERS spectra
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and metallic nanoparticles used in SERS enhancing the intrinsically weak Raman signal
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by 106⁓1014 orders of magnitude31,32. Gold nanoparticles (Au NPs) possess
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extraordinary SERS activities and have been successfully employed as SERS-active
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substrates. Here, we prepared gold nanoparticles (AuNPs) within MIL-101, a highly
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porous and thermally stable metal−organic framework (MOF) which is expected to
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provide the AuNPs with much better stability, by an in-situ reduction strategy. The
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AuNPs within MIL-101 were denoted as AuNPs@MIL-101 as the SERS enhanced
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substrate and was firstly used to enhance the Raman signal of TMB2+.
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Naturally, the as-prepared BNLISA platform was low-cost, fast, highly sensitive,
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and excellently stable, which also acted as a model for other pesticides detection. The
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fabrication and detection process of the proposed BNLISA are illustrated in Scheme. 1.
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EXPERIMENTAL SECTION
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Materials and apparatus
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Triazophos. Parathion, triadimefon, Methomyl, trichlorfon, methamidophos,
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Malathion and Omethoate (Dr Ehrenstorfer Gmbh Augsburg, Germany). Methacrylic 5
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acid (MAA), trimethylolpropane trimethacrylate (TRIM) (Alfa Aesar Massachusetts,
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USA). Free radical initiator 2,2-azobisiso-butyronitrile (AIBN) (no. 4 reagent and H.
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V. Chemical Co., Ltd. Shanghai, China). Ionic liquid 1-butylpyridinium
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hexafluorophosphate (BPPF6, 99% purity) (Lanzhou Greenchem, Lanzhou, China).
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Chromium (III) nitrate (Cr (NO3)3·9H2O), 1,4-benzene dicarboxylic acid (H2BDC),
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hydrogen tetrachloroaurate trihydrate (HAuCl4·3H2O, > 99.9%), trisodium citrate
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sodium and citrate dehydrate (Sigma-Aldrich St. Louis, MO, USA). N-
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Dicyclohexylcarbodiimide (DCC) and N-hydroxysuccinate (NHS), Bovine serum
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albumin (BSA) and polyethylene glycol (PEG) 20000 (Sigma-Aldrich St. Louis, MO,
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USA), Triazophos hapten (Institute of Pesticide and Environmental Toxicology,
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Zhejiang University, China). 3, 3´, 5, 5´-tetramethylbenzidine (TMB) ELISA substrate
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(TransGen Biotech Co., Ltd. Beijing, China). All the other chemicals and organic
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solvents used in this study were of the highest available purity and at least of analytical
127
grade. Maxisorp polystyrene 96-well plates were obtained from Corning, Inc. (Corning,
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NY, USA).
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Maxisorp polystyrene 96-well plates (Corning, Inc. Corning, NY, USA). Ultrapure
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water (≥ 18.2 MΩ) produced by a Milli-Q water purification system (Millipore, Bedford,
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MA, USA) was used in all e experimental works. UV absorbance was recorded using a
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Lab systems 96-well plate reader (TECAN, Switzerland) in dual-wavelength mode
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(450–650 nm). Scanning electron microscopy (SEM) images were undertaken with a
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SEM instrument (SU8020, Hitachi, Japan). Scanning electron microscopy (TEM)
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images were undertaken with a TEM instrument (JEM 1200EX, JEOL). The type and 6
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relative content of element and the chemical environment surrounding the element were
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tested by X-ray photoelectron spectroscopy (XPS, Thermo escalab 250X, USA) with
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Al Kα radiation as the excitation source. The XPS binding energies were adjusted by
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interior label carbon (C 1s = 284.8 eV), and the other positions of peaks were calibrated
140
depending on the C 1s peak. Matrix-Assisted Laser Desorption/Ionization Time of
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Flight Mass Spectrometry (MALDI-TOF-MS, ABI 4800Plus, USA).
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Preparation of biomimetic 96-well MIPs array plate.
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The preparation of MIP nanoparticles by precipitation polymerization using
144
triazolone as a template has been studied in detail in our laboratory33. The concise
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synthesis process of MIPs, non-imprinted polymers (NIPs) and the preparation process
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of the biomimetic 96-well MIPs array plate (Scheme. 1a and Scheme. 1c) are supplied
147
in Supporting Information.
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Preparation of SERS-enhanced substrate Au NPs@MIL-101
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MIL-101 and Au NPs@MIL-101 were synthesized (Scheme 1d) according to a
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previously reported work with appropriate modifications34, 35, and the synthesis process
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is supplied in the Supporting Information.
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Preparation of the Pt@BSA hapten probe
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Synthesis of BSA-hapten
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BSA-hapten conjugates were synthesized by carbodiimide method between amino
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groups from BSA and carboxyl groups from hapten compounds and identified by UV
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spectroscopy. Firstly, hapten of triazophos (27.37 mg, 0.1 mmol) and NHS (34.5 mg,
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0.3 mmol) were dissolved in 0.5 mL DMF and the mixture was stirred for 15 min by 7
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magnetic stirring, getting solution (a). Then, DCC (30.92 mg, 0.15 mmol) were
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dissolved in 0.5 mL DMF, and the solution was added in the solution (a) drop by drop,
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getting solution (b). The solution (b) was stirred over-night at room temperature with
161
avoiding meeting up. Through above steps, the carboxyl groups of the hapten
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compounds were activated. Solution (b) was centrifugated (5000 rpm, 10min) to
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received activated hapten supernatant solution and was added dropwise in BSA solution
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which was obtained by weighing 60 mg BSA in 5 mL carbonate buffer solution (CBS
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0.01 M pH=9.6) and then stirred for 4h at room temperature to achieve BSA-hapten
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conjugates. Finally, the BSA-hapten conjugated solution was dialyzed against
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phosphate buffered solution (PBS 0.01 M pH=7.4) for 3 days to remove the unbound
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hapten. After purifying, the BSA-hapten conjugated solution was mixed glycerol with
169
the same volume and stored at -20 ℃ before use, and was identified by UV spectroscopy
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and MALDI-TOF-MS (Matrix-Assisted Laser Desorption/Ionization Time of Flight
171
Mass Spectrometry).
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Synthesis of Pt NPs
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The Pt NPs were synthesized according to a previously described method36, and
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the synthesis process is supplied in the Supporting Information. The obtained Pt NPs
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were identified by TEM.
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Preparation of Pt@BSA-hapten probe
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The pH value of the Pt NPs solution (1 mL) was adjusted to 5.4 with 20 μL K2CO3
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(0.1 mol⁓L-1), and then different volume of BSA-hapten solution was introduced into
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the colloidal solution. After with standing for 12 h, the solution was centrifuged for 60 8
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min at 10000 rpm and the precipitate was dissolved with 1 mL PBS (0.01 M pH=7.4)
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including 1% PEG 20000 for three times to remove the unbound BSA-haptens.
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Thereafter, concentrate as the Pt@BSA-hapten probes were resuspended in 200 μL of
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PBS (0.01 M pH=7.4) including 1% PEG 20000 and stored at 4 ℃. The achieved
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Pt@BSA-hapten probes were identified by UV spectroscopy and TEM.
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Competitive BNLISA for triazophos detection based on colorimetric and SERS
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methods
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As shown in Scheme. 1c, the detection procedure was carried out using the
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molecular imprinted film on the 96-well array plate after washing three times with
189
PBST (PBS with 0.05% (v/v) Tween 20). Firstly, 50 μL of triazophos standard solution
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diluted in Tris-HCl (0.01 M, pH 3.7) and 50 μL of Pt@BSA-hapten probe solution
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diluted in Tris-HCl (0.01 M, pH 3.7) were sequentially added to the microplate. During
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incubation for 1 h at room temperature, hapten coating on the Pt@BSA-hapten probe
193
and triazophos competed for binding with the recognition site on the surface of the
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MIPs. The unbound pesticide molecules and Pt@BSA-hapten probes were removed by
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three washes with PBST. Then, 100 μL of TMB ELISA substrate was added to the
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microplate and incubated for 15 min at room temperature, accompanied by the change
197
from TMB to the radical cation TMB2+. The reaction was terminated by adding 50 μL
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of H2SO4 (2 mol⁓L-1) to each well. Finally, absorbance (450 nm) signals were recorded
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by a Lab Systems 96-well plate reader (TECAN, Switzerland). Importantly, the radical
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cation TMB2+ solution was assessed by SERS without adding H2SO4 (2 mol⁓L-1).
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Firstly, 20 μL of TMB2+ solution was mixed with 200 μL of the Au NPs@MIL-101 9
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substrate, incubated for 60 s, and then the SERS “fingerprint” information was
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measured by a portable Raman spectrometer (RT5000, TSINGHUA TONGFANG, Bei
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Jing, China) with a 785 nm laser as the excitation source. The SERS measurement was
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carried out within the wavelength range of 350–2000 cm–1. The acquisition time was
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set to 40 s.
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RESULTS AND DISCUSSION
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Preparation and characterization of MIPs and NIPs
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To obtain MIP nanoparticles with a uniform particle size and an increased
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number of effective recognition sites, the type of monomer and cross-linker, the ratio
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of template to monomer and cross-linker, and the kind and volume of dispersing solvent
212
should be optimized. Based on the results of our laboratory studies, the best outcome
213
was obtained when using a 1:6:10 ratio of template, monomer, and cross-linker and 20
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mL of acetonitrile as the dispersing solvent. The surface morphology of the synthesized
215
MIPs and NIPs was characterized by SEM, as shown in Figure. 1a-b. Uniform MIPs
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microspheres was obtained and more folds on surface was observed on MIPs in the
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SEM images than NIPs.
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Preparation and characterization of Au NPs@MIL-101.
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The TEM image shown in Figure. S1a-b clearly indicates that the Au NPs were
220
embedded inside MIL-101. The elemental composition of Au NPs@MIL-101 was
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characterized by X-ray photoelectron spectroscopy (XPS), as shown in Figure. S1c.
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These revealed the successful formation of Au NPs@MIL-101 SERS enhanced
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substrate. 10
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Moreover, the SERS activity of the Au NPs@MIL-101 nanoparticles was
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quantified and compared to those of Au NPs prepared under the same synthetic
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conditions as Au NPs@MIL-101. As shown in Figure. 2a, both the Au NPs and Au
227
NPs@MIL-101 produced strong SERS signals corresponding to TMB2+. In contrast,
228
MIL-101 did not produce any detectable SERS signals, indicating that the SERS
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enhancement ability originated from the Au NPs. Although the Au NPs themselves
230
could produce detectable SERS signals, they were not stable. As shown in Figure. 2b,
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the intensity of the SERS signal at 558 cm-1 decreased with time. MIL-101, with high
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porosity and thermal stability, was chosen as a protecting matrix to prevent aggregation
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of the Au NPs. The Au NPs@MIL-101 exhibited a stable SERS signal at 558cm-1 as
234
shown in Figure. 2c. The reproducibility of the Au NPs@MIL101 substrate was also
235
evaluated, as shown in Figure. 2d. In this figure, the black line indicates the average
236
intensity of the SERS signal at 558 cm-1 and the values of the intensity deviation (D)
237
was calculated to be less than 12% and the definition of D was as shown in Supporting
238
Information. Therefore, Au NPs@MIL-101 was selected as the SERS enhanced
239
substrate in the followed experiments. Moreover, the SERS spectra of TMB and TMB2+
240
was proposed as shown in Figure S2, and the characteristic absorption peaks of TMB2+
241
were assigned in Table S1 in Supporting Information.
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Preparation and optimization of the Pt@BSA-hapten probe
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The Pt@BSA-hapten probe consisted of three key parts: target hapten, BSA and
244
Pt NPs. The TEM image in Figure. 1c showed that the prepared Pt NPs exhibited
245
consistent diameter and did not aggregate. As shown in Figure. 1d, after modification 11
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with hapten, the maximum absorbance peak of BSA shifted from 278 nm to 268 nm.
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Furthermore, the conjugation ratio between hapten of triazophos and BSA was 21.3: 1
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that was measured by MALDI-TOF-MS as shown in Figure. S3. Pt NPs were combined
249
with BSA through thiol groups and abundant groups on BSA. To form a solid
250
combination, the pH of the Pt NP colloid solution was adjusted to 4.8, 5.1, and 5.4 near
251
the pI of BSA37. As shown in Figure. 1d, after modification with BSA-hapten, the Pt
252
NPs solution showed the characteristic peak of BSA-hapten at 271 nm.
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Optimization of the working buffer solutions
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The prepared Pt@BSA-hapten solution needed to be diluted before use. The dilute
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buffer solution, named the working buffer solution, influenced the assay sensitivity by
256
changing the characteristics of the analyte solution or affecting the interactions between
257
the MIP recognition sites and the hapten. PBS (0.01 M, pH=4.22), Tris-HCl (0.05 M,
258
pH=4.30), CBS (0.05 M, pH=4.22) and ABS (0.01 M, pH=4.10) were selected for study.
259
In this work, the inhibition rate was used to evaluate the performance of the assays. The
260
inhibition rate (IC (%)) of targets at various volumes was calculated and the definition
261
of IC (%) was as shown in Supporting Information. The dilute buffer solutions were
262
optimized by comparing IC (%). As shown in Figure. 3d, the IC (%) reached a
263
maximum when the dilute buffer solution was Tris-HCl (0.01 mol/L, pH=4.30).
264
Optimization of concentration of the BSA-hapten
265
The concentration of the BSA-hapten mixed in Pt colloid solution had great
266
influence on the detection sensitivity and the linear range of competition reactions. The
267
Pt@BSA-hapten probes were prepared by adding 5 μL, 10 μL, 15 μL, 20 μL and 25 μL 12
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of BSA-hapten solution in 1 mL of Pt NPs solution at final concentrations of 33.9
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μg·mL-1, 67.8 μg·mL-1, 101.7 μg·mL-1, 135.6 μg·mL-1, 169.5 μg·mL-1. As the results
270
shown in Figure. 3e, the IC (%) increased accordingly as the concentration increased
271
from 33.9 μg·mL-1 to 67.8 μg·mL-1, and shown a decrease trend as the concentrate
272
continued to increase to 169.5 μg·mL--1. In addition, the TEM images of the Pt@BSA-
273
hapten were provided (Figure. 3a-c) when the concentration of BSA-hapten were 67.8
274
μg·mL-1, 169.5 μg·mL-1 and 678 μg·mL-1. The particle size increased of the
275
composition with the increase of concentration of BSA-hapten, On the one hand, the
276
phenomenon demonstrated the interaction between BSA-hapten and Pt NPs, and on the
277
other hand that explained that why the IC (%) decreased gradually from 67.8 μg·mL-1
278
to 169.5 μg·mL-1. We inferred that the increasing particle produced large steric
279
hindrance that interfered the competition process. Above all, BSA-hapten of 67.8
280
μg·mL-1 was used in subsequent experiments.
281
Optimization of the pH of Tris-HCl
282
The pH value of Tris-HCl was an important factor for the assay. The pH of Tris-
283
HCl (0.05 M) was adjusted in the range of 2.0 – 6.0. As shown in Figure. 3f, we found
284
that the IC (%) increased with the pH from 2.1 to 3.7 and then decreased with the pH
285
from 4.3 to 6.1. The IC (%) was observed to reach a maximum at pH 3.7. Hence, we
286
selected pH 3.7 as the optimum pH for all subsequent experiments. The pKa of the
287
monomer methacrylic acid (MAA) was 5.5; therefore, when the solution pH was 3.7,
288
the imprinted membrane was protonated. Furthermore, at this pH, the surface charge of
289
BSA was positive because its pI is 4.7. Triazophos is a compound with an electron-rich 13
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structure and thus should combine readily with the protonated imprinted membrane.
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Analytical performance of the proposed BNLISA method
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Under the optimal conditions mentioned above, we tested the potential application
293
of competitive BNLISA to triazophos detection by colorimetric and SERS methods.
294
For the colorimetric method, the intensity of the absorbance at 450 nm gradually
295
decreased with increasing triazophos concentration in the range from 0 to 10000 ng·mL-
296
1
297
inhibition rate and the logarithm of the triazophos concentration in the concentration
298
range of 5-1000 ng·mL-1, with a calibration curve of y=34.993 Log c – 21.9 (R2 =
299
0.9641). The limit of detection (LOD) was 1 ng·mL-1. For the SERS method, Figure.
300
4c shows that the intensity of a number of Raman peaks corresponding to TMB2+
301
decreased with increasing triazophos concentration (0-10000 ng·mL-1). For the
302
intensity of the SERS signal at 558 cm-1, a good linear relationship with triazophos
303
concentration was also obtained, with a calibration curve of y=-736.43 Log c + 3962.3
304
(R2 = 0.9707), as shown in Figure. 4d. The concentration range of triazophos detected
305
by the SERS method was 1-10000 ng·mL-1, which was wider than the range detected
306
by the colorimetric method. The LOD was also 1 ng·mL-1.
(Figure. 4a). As shown in Figure. 4b, there was a good linear relationship between the
307
The recognizing selectivity of the competitive BNLISA were investigated by
308
cross- reactivity studies between the target and analogues of target as shown in Table
309
1. The cross-reactivity rate (CR%) was calculated by the followed Eq: CR% = (IC50
310
(triazophos) /
311
of the compounds containing phosphoester and phosphorothioate groups ((5), (6), (7)
IC50 (Structural analogues)) × 100%. From the results, we found that the IC50 values
14
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and (8)) were lower than those of the compounds that did not contain these functional
313
groups ((2), (3) and (4)). As a result, we concluded that the phosphorothioate played a
314
very important role in the competition between the target and the Pt@BSA-hapten
315
probe for the binding sites on the MIPs. Both the hapten structure and the selective
316
adsorption ability of the MIPs contributed to the selectivity of the BNLISA. The cross-
317
reactivity studies also showed the selectivity of MIPs were better than the selectivity of
318
NIPs.
319
The properties of the proposed competitive BNLISA were also compared with
320
those of previously reported methods for detecting triazophos, as shown in Table 2. The
321
table shows that the proposed BNLISA for detecting triazophos is a novel, simple and
322
sensitive method.
323
Real Sample Analysis
324
To evaluate the accuracy of BNLISA in real samples, water samples spiked at 10,
325
100, and 500 µg·kg-1 were investigated and pear samples spiked at 20, 100, and 500
326
µg/kg were investigated (with three replicates for each concentration and the sample
327
treatment method as shown in Supporting Information). The results are shown in Table
328
3. The recovery of the BNLISA ranged from 75.6 to 109.8% for the colorimetric
329
method and from 65.6 to 110.7% for the SERS method, with RSDs ranging from 7.8 to
330
9.4% and 10.1 to 15.2%, respectively. The results were in good agreement with the
331
values recorded by HPLC–MS/MS method (Supporting Information). And, these
332
indicated the BNLISA is a practical and accurate method for the detection of triazophos
333
in water and pear samples. 15
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334
In summary, a competitive BNLISA for rapid determination of triazophos was
335
constructed. For the low-cost, sensitive and simple method, three major advantages
336
could be concluded: (1) A good performance of 96-well biomimetic MIPs array plate
337
was designed by immobilized MIPs uniformly onto plate by “grafting to” method; (2)
338
The Pt@BSA-hapten probe was proposed instead of HRP-hapten probe benefiting from
339
the peroxidase-like activity of platinum nanoparticles (Pt NPs) and the “bridge”
340
function of bovine serum albumin (BSA) for linking Pt NPs and target hapten. (3) The
341
Au NPs@MIL-101 of SERS enhanced substrate for sensing TMB2+was synthesized
342
successfully. This new strategy is promising for the rapid detection of pesticide residues
343
in the environment with wide working range and low detection limit, and provided a
344
potential method to monitor the other small molecules detection.
345
ASSOCIATED CONTENT
346
Supporting Information
347
Preparation of biomimetic MIPs 96-well array plate.
348
Preparation of SERS enhancement substrate Au NPs@MIL-101.
349
Synthesis of Pt NPs.
350
Sample treatment and HPLC-MS/MS method.
351
Additional tables and figures.
352
AUTHOR INFORMATION
353
Corresponding Authors
354
*E-mail:
[email protected] 355
[email protected] 16
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Notes
357
The authors declare no competing financial interest.
358
ACKNOWLEDGMENTS
359
This work was supported by National Natural Science Foundation of China (contact
360
No. 31471654, 31772071, 31501571) and the China Agriculture Research System (NO.
361
CARS-05-05A-03).
362 363 364 365 366 367 368 369 370 371 372 373 374 375 376 377 17
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Legends
524
Scheme 1. Representative illustration of the design strategy and fabrication process of
525
competitive BNLISA.
526
Figure 1. Analysis and characterization of MIPs/NIPs and Pt@BSA-hapten probe.
527
Figure 2. Analysis enhanced ability of Au NPs@MIL-101 for SERS signal.
528
Figure 3. Optimization of the competition conditions for BNLISA.
529
Figure 4. Analytical performance of the competitive BNLISA.
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Tables
531
Table 1. Cross- reactivity studies between triazophos and structural analogues.
polarization
immunoassay
for
simultaneous
detection
of
24
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Table 2. Comparison of various methods for triazophos detection.
533
Table 3. Results of the detection of triazophos in water samples by the proposed method.
534
25
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Figures
Scheme 1. Representative illustration of the design strategy and fabrication process of competitive BNLISA. (a). Synthesis of MIP microspheres; (b). Fabrication of Pt@BSA-hapten signal probe; (c). Design of competitive BNLISA; (d). Synthesis of the SERS-enhanced substrate Au NPs@MIL-101.
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Figure 1. Analysis and characterization of MIPs/NIPs and Pt@BSA-hapten probe. (a). SEM of MIPs; (b). SEM of NIPs; (c). TEM of Pt NPs; (d). UV–vis absorption spectra of Pt NPs, BSA, BSA-hapten and Pt@BSA-hapten.
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Figure 2. Analysis enhanced ability of Au NPs@MIL-101 for SERS signal. (a) SERS spectra of TMB2+ with Au NPs, Au NPs@MIL-101 and MIL-101; (b) The varieties of Raman signals of TMB2+ from 0 to 9 min for Au NPs substrate; (c) The varieties of Raman signals of TMB2+ from 0 to 9 min for Au NPs@MIL-101 substrate; (d) The relative intensity of SERS signals at 558 cm-1 from 13 different batches Au NPs@MIL101.
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Figure 3. Optimization of the competition conditions for BNLISA. (a). TEM of Pt@BSA-hapten with BSA-hapten of 67.8 μg·mL-1 ; (b). TEM of Pt@BSA-hapten with BSA-hapten of 169.5 μg·mL-1; (c). TEM of Pt@BSA-hapten with BSA-hapten of 678 μg·mL-1. Optimization of assay conditions for detection of triazophos; (d). Different work buffer solution; (e) different concentration of the BSA-hapten; (f). Different pH of work buffer solution.
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Figure 4. Analytical performance of the competitive BNLISA. (a). UV–vis absorption spectra for triazophos detection in the concentration range of 0 – 10000 ng·mL-1 with the colourimetric method; (b). Calibration curve obtained from the absorbance values at 450 nm; (c). SERS spectra for triazophos detection in the concentration range of 0 – 10000 ng·mL-1 with the SERS method; (d). Calibration curve obtained from the SERS signal intensity at 558 cm-1.
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Tables Table 1. Cross- reactivity studies between triazophos and structural analogues
MIPs Analogues
Structure
NIPs
IC50 (ng·mL-1)
CR (%)
IC50 (ng·mL-1)
CR (%)
Triazophos (1)
112
100
1513
100
Methomyl (2)
> 106
< 0.01
> 103.5
< 49
Triazolone (3)
> 106
< 0.01
> 103.5
< 49
Carbaryl (4)
> 106
< 0.01
> 106.0
< 0.01
Trichlorfon (5)
> 103.8
< 1.8
103.2
93
Parathion (6)
> 103.8
< 1.8
> 103.5
< 49
Methamidophos (7)
> 103.8
< 1.8
> 103.5
< 49
Chlorpyrifos (8)
> 103.8
< 1.8
> 103.5
< 49
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Table 2. Comparison of various methods for triazophos detection
Linear range Assay format
LOD
Method
Ref -1
-1
(ng⸱mL )
(ng⸱mL )
0.98 - 8.29
0.096
38
Colorimetric
-
50
39
fluorescence
40 - 200
40
40
fluorescent polarization immunoassay
fluorescence
16.09 - 511.84
5.86
41
Competitive-BELISA
Colorimetric
0.001 - 10000
0.001
12
Colorimetric
5 – 1000
1
This
SERS
1 – 10000
1
work
surface plasmon Non-competitive direct SPR immunosensor resonance competitive gold immunochromatographic assay competitive fluorescence polarization immunoassays
Competitive-BNLISA
Table 3. Results of the detection of triazophos in water samples by the proposed method
Sample
Water
Pear
Recoveries/RSD (%)
Spiking concentration (µg·kg-1)
Colourimetric
SERS
HPLCMS/MS
10
92.0/7.8
80.5/10.1
99.7/2.3
100
103.4/8.1
97.9/10.9
103.2/1.4
500
109.8/9.4
110.7/13.7
100.8/1.2
20
78.4/11.2
65.6/15.2
89.8/.1.0
100
75.6/9.8
80.2/13.5
98.2/2.1
500
81.2/9.3
76.3/11.8
101/2.6
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Graphical Abstract: Competitive Biomimetic Nanozyme-Linked Immunosorbent Assay for Colorimetric and SERS Sensing of small molecular.
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