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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**

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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

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3Department

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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]

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**(J.

W.) Tel: +86 10 82106568; Fax: +86 10 82106568. E-mail: [email protected]

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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

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molecularly imprinted polymers (MIPs). However, enzymes labels used in BELISA

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still suffer some drawbacks such as high production cost and limited stability. To

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overcome the drawbacks, a biomimetic nanozyme-linked immunosorbent assay

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(BNLISA) based on MIPs and nanozyme labels was first proposed. For nanozyme

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labels, Pt NPs (platinum nanoparticles) acted as peroxidase by catalysing the oxidation

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of colourless 3,3′,5,5′-tetramethylbenzidine (TMB) into an ideal SERS marker—blue

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TMB2+ and BSA-hapten (bovine serum albumin-hapten) showed superior selectivity

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when competing with targets for binding sites on MIPs, which named Pt@BSA-hapten

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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

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enzymes with nanozymes for combination with MIPs may bring about a new prospect

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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

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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

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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

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antibodies for small molecule detection via the ELISA method, biomimetic ELISA

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(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

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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

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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

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(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

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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

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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

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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

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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

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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

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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

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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

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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

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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

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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

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should be optimized. Based on the results of our laboratory studies, the best outcome

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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

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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

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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

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NPs@MIL-101 produced strong SERS signals corresponding to TMB2+. In contrast,

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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

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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

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shown in Figure. 2c. The reproducibility of the Au NPs@MIL101 substrate was also

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evaluated, as shown in Figure. 2d. In this figure, the black line indicates the average

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intensity of the SERS signal at 558 cm-1 and the values of the intensity deviation (D)

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was calculated to be less than 12% and the definition of D was as shown in Supporting

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Information. Therefore, Au NPs@MIL-101 was selected as the SERS enhanced

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substrate in the followed experiments. Moreover, the SERS spectra of TMB and TMB2+

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was proposed as shown in Figure S2, and the characteristic absorption peaks of TMB2+

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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

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Pt NPs. The TEM image in Figure. 1c showed that the prepared Pt NPs exhibited

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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

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with BSA through thiol groups and abundant groups on BSA. To form a solid

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combination, the pH of the Pt NP colloid solution was adjusted to 4.8, 5.1, and 5.4 near

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the pI of BSA37. As shown in Figure. 1d, after modification with BSA-hapten, the Pt

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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

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changing the characteristics of the analyte solution or affecting the interactions between

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the MIP recognition sites and the hapten. PBS (0.01 M, pH=4.22), Tris-HCl (0.05 M,

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pH=4.30), CBS (0.05 M, pH=4.22) and ABS (0.01 M, pH=4.10) were selected for study.

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In this work, the inhibition rate was used to evaluate the performance of the assays. The

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inhibition rate (IC (%)) of targets at various volumes was calculated and the definition

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of IC (%) was as shown in Supporting Information. The dilute buffer solutions were

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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).

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Optimization of concentration of the BSA-hapten

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The concentration of the BSA-hapten mixed in Pt colloid solution had great

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influence on the detection sensitivity and the linear range of competition reactions. The

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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

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shown in Figure. 3e, the IC (%) increased accordingly as the concentration increased

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from 33.9 μg·mL-1 to 67.8 μg·mL-1, and shown a decrease trend as the concentrate

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continued to increase to 169.5 μg·mL--1. In addition, the TEM images of the Pt@BSA-

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hapten were provided (Figure. 3a-c) when the concentration of BSA-hapten were 67.8

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μg·mL-1, 169.5 μg·mL-1 and 678 μg·mL-1. The particle size increased of the

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composition with the increase of concentration of BSA-hapten, On the one hand, the

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phenomenon demonstrated the interaction between BSA-hapten and Pt NPs, and on the

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other hand that explained that why the IC (%) decreased gradually from 67.8 μg·mL-1

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to 169.5 μg·mL-1. We inferred that the increasing particle produced large steric

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hindrance that interfered the competition process. Above all, BSA-hapten of 67.8

280

μg·mL-1 was used in subsequent experiments.

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Optimization of the pH of Tris-HCl

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The pH value of Tris-HCl was an important factor for the assay. The pH of Tris-

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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

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from 4.3 to 6.1. The IC (%) was observed to reach a maximum at pH 3.7. Hence, we

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selected pH 3.7 as the optimum pH for all subsequent experiments. The pKa of the

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monomer methacrylic acid (MAA) was 5.5; therefore, when the solution pH was 3.7,

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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.

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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

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(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

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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) /

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of the compounds containing phosphoester and phosphorothioate groups ((5), (6), (7)

IC50 (Structural analogues)) × 100%. From the results, we found that the IC50 values

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and (8)) were lower than those of the compounds that did not contain these functional

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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

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adsorption ability of the MIPs contributed to the selectivity of the BNLISA. The cross-

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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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356

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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References

381

(1) Chen, L. X.; Wang, X. Y.; Lu, W. H.; Wu, X. Q.; Li, J. H. Molecular imprinting:

382

perspectives and applications. Chem. Soc. Rev. 2016, 45, 2137-2211.

383

(2) Pan, J. M.; Chen, W.; Ma, Y.; Pan, G. Q. Molecularly imprinted polymers as

384

receptor mimics for selective cell recognition. Chem. Soc. Rev. 2018, 47, 5574-5587.

385

(3) Masque, N.; Marce, R. M.; Borrull, F.; Cormack, P. A. G.; Sherrington, D.C.

386

Synthesis and evaluation of a molecularly imprinted polymer for selective on-line solid-

387

phase extraction of 4-nitrophenol from environmental water. Anal. Chem. 2000, 72,

388

4122-4126.

389

(4) Zhao, T.; Guan, X. J.; Tang, W. J.; Ma, Y.; Zhang, H. X. Preparation of temperature

390

sensitive molecularly imprinted polymer for solid-phase microextraction coatings on

391

stainless steel fiber to measure ofloxacin. Anal. Chim. Acta. 2015, 853, 668-675.

392

(5) Udomsap, D.; Branger, C.; Culioli, G.; Dollet, P.; Brisset, H. A versatile

393

electrochemical sensing receptor based on a molecularly imprinted polymer. Chem.

394

Commun. 2014, 50 7488-7491.

395

(6) Li, S. H.; Yin, G. H.; Zhang, Q.; Li, C. L.; Luo, J. H.; Xu, Z.; Qin, A. L. Selective

396

detection of fenaminosulf via a molecularly imprinted fluorescence switch and silver

397

nano-film amplification. Biosens. Bioelectron. 2015, 71, 342-347.

398

(7) Farka, Z.; Cunderlova, V.; Horackova, V.; Pastucha, M.; Mikusova, Z.; Hlavacek,

399

A.; Skladal, P. Prussian Blue Nanoparticles as a Catalytic Label in a Sandwich 18

ACS Paragon Plus Environment

Page 19 of 33

Journal of Agricultural and Food Chemistry

400

Nanozyme-Linked Immunosorbent Assay. Anal. Chem. 2018, 90, 2348-2354.

401

(8) Piletsky, S. A.; Piletska, E. V.; Chen, B. N.; Karim, K.; Weston, D.; Barrett, G.;

402

Lowe, P.; Turner, A. P. F. Chemical grafting of molecularly imprinted homopolymers

403

to the surface of microplates. Application of artificial adrenergic receptor in enzyme-

404

linked assay for beta-agonists determination. Anal. Chem. 2000,72, 4381-4385.

405

(9) Chianella, I.; Guerreiro, A.; Moczko, E.; Caygill, J. S.; Piletska, E. V.; Sansalvador,

406

I. M. P. D.; Whitcombe, M. J.; Piletsky, S. A. Direct Replacement of Antibodies with

407

Molecularly Imprinted Polymer Nanoparticles in ELISA-Development of a Novel

408

Assay for Vancomycin. Anal. Chem. 2013, 85, 8462-8468.

409

(10) Tang, Y. W.; Fang, G. Z.; Wang, S.; Sun, J. W.; Qian, K. Rapid Determination of

410

Metolcarb Residues in Foods Using a Biomimetic Enzyme-Linked Immunosorbent

411

Assay Employing a Novel Molecularly Imprinted Polymer Film as Artificial Antibody.

412

J. Aoac. Int. 2013, 96, 453-458.

413

(11) Bi, X. D.; Liu, Z. Facile Preparation of Glycoprotein-Imprinted 96-Well

414

Microplates for Enzyme-Linked Immunosorbent Assay by Boronate Affinity-Based

415

Oriented Surface Imprinting. Anal. Chem. 2014, 86, 959-966.

416

(12) Hong, S. H.; She, Y. X.; Cao, X. L.; Wang, M.; Zhang, C.; Zheng, L. F.; Wang, S.

417

S.; Ma, X. B.; Shao, H.; Jin, M. J.; Jin, F.; Wang, J. Biomimetic enzyme-linked

418

immunoassay based on a molecularly imprinted 96-well plate for the determination of

419

triazophos residues in real samples. Rsc. Adv. 2018, 8, 20549-20556.

420

(13) Li, L.; Peng, A. H.; Lin, Z. Z.; Zhong, H. P.; Chen, X. M.; Huang, Z. Y. Biomimetic

421

ELISA detection of malachite green based on molecularly imprinted polymer film. 19

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 20 of 33

422

Food Chem. 2017, 229, 403-408.

423

(14) Sun, Q.; Xu, L. H.; Ma, Y.; Qiao, X. G.; Xu, Z. X. Study on a biomimetic enzyme-

424

linked immunosorbent assay method for rapid determination of trace acrylamide in

425

French fries and cracker samples. J. Sci. Food. Agr. 2014, 94, 102-108.

426

(15) Shi, C.; Liu, X. Y.; Song, L. Y.; Qiao, X. G.; Xu, Z. X. Biomimetic Enzyme-linked

427

Immunosorbent Assay Using a Hydrophilic Molecularly Imprinted Membrane for

428

Recognition and Fast Determination of Trichlorfon and Acephate Residues in

429

Vegetables. Food Anal, Method. 2015, 8, 2496-2503.

430

(16) Wang, Q. Q.; Wei, H.; Zhang, Z. Q.; Wang, E. K.; Dong, S. J. Nanozyme: An

431

emerging alternative to natural enzyme for biosensing and immunoassay. Trac-Trend.

432

Anal. Chem. 2018, 105, 218-224.

433

(17) Gao, L. Z.; Zhuang, J.; Nie, L.; Zhang, J. B.; Zhang, Y.; Gu, N.; Wang, T. H.;

434

Feng, J.; Yang, D. L.; Perrett, S.; Yan, X. Intrinsic peroxidase-like activity of

435

ferromagnetic nanoparticles. Nat. Nanotechnol. 2007, 2, 577-583.

436

(18) He, W. W.; Liu, Y.; Yuan, J. S.; Yin, J. J.; Wu, X. C.; Hu, X. N.; Zhang, K.; Liu,

437

J.B.; Chen, C. Y.; Ji, Y. L.; Guo, Y. T. Au@Pt nanostructures as oxidase and peroxidase

438

mimetics for use in immunoassays. Biomaterials 2011, 32, 1139-1147.

439

(19) Borodko, Y.; Thompson, C. M.; Huang, W. Y.; Yildiz, H. B.; Frei, H.; Somorjai,

440

G.A.

441

Compounds: Structure and Stability. J. Phys. Chem. C. 2011, 115, 4757-4767.

442

(20) Knecht, M. R.; Weir, M. G.; Myers, V. S.; Pyrz, W. D.; Ye, H. C.; Petkov, V.;

443

Buttrey, D. J.; Frenkel, A. I.; Crooks, R. M. Synthesis and Characterization of Pt

Spectroscopic Study of Platinum and Rhodium Dendrimer (PAMAM G4OH)

20

ACS Paragon Plus Environment

Page 21 of 33

Journal of Agricultural and Food Chemistry

444

Dendrimer-Encapsulated Nanoparticles: Effect of the Template on Nanoparticle

445

Formation. Chem. Mater. 2008, 20, 5218-5228.

446

(21) Wang, X.Y.; Zhang, Y.C.; Li, T.F.; Tian, W.D.; Zhang, Q.; Cheng, Y.Y.

447

Generation 9 Polyamidoamine Dendrimer Encapsulated Platinum Nanoparticle Mimics

448

Catalase Size, Shape, and Catalytic Activity. Langmuir 2013, 29, 5262-5270.

449

(22) Li, W.; Bin, C.; Zhang, H. X.;

450

stabilized Pt nanozyme for peroxidase mimetics and its application on colorimetric

451

detection of mercury(II) ions. Biosens. Bioelectron. 2015, 66, 251-258.

452

(23) Ke, H.; Zhang, X.; Huang, C. S.; Jia, N. Q. Electrochemiluminescence evaluation

453

for carbohydrate antigen 15-3 based on the dual-amplification of ferrocene derivative

454

and Pt/BSA core/shell nanospheres. Biosens. Bioelectron. 2018, 103, 62-68.

455

(24) Zhang, A. M.; Huang, C. S.; Shi, H.Y.; Guo, W. W.; Zhang, X.; Xiang, H. K.; Jia,

456

T.; Miao, F.; Jia, N. Q. Electrochemiluminescence immunosensor for sensitive

457

determination of tumor biomarker CEA based on multifunctionalized Flower-like

458

Au@BSA nanoparticles. Sensor. Actuat. B-Chem. 2017, 238, 24-31.

459

(25) Goswami, N.; Giri, A.; Bootharaju, M. S.; Xavier, P. L.; Pradeep, T.; Pal, S. K.;

460

Copper Quantum Clusters in Protein Matrix: Potential Sensor of Pb2+ Ion. Anal. Chem.

461

2011, 83, 9676-9680.

462

(26) Yao, T.; Gu, X.; Li, T. F.; Li, J. G.; Li, J.; Zhao, Z.; Wang, J.; Qin, Y. C.; She, Y.

463

X. Enhancement of surface plasmon resonance signals using a MIP/GNPs/rGO nano-

464

hybrid film for the rapid detection of ractopamine. Biosens. Bioelectron. 2016, 75, 96-

465

100.

Sun, Y. H.; Wang, J.; Zhang, J. L.; Fu, Y. BSA-

21

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 22 of 33

466

(27) Zhu, X. D.; Zeng, Y. B.; Zhang, Z. L.; Yang, Y. W.; Zhai, Y. Y.; Wang, H. L.;

467

Liu, L. Y.; Hu, J.; Li, L. A new composite of graphene and molecularly imprinted

468

polymer based on ionic liquids as functional monomer and cross-linker for

469

electrochemical sensing 6-benzylaminopurine. Biosens. Bioelectron. 2018, 108, 38-45.

470

(28) Chen, C.; Wang, Y. H.; Zhao, X. P.; Wang, Q.; Qian, Y. Z. The combined toxicity

471

assessment of carp (Cyprinus carpio) acetylcholinesterase activity by binary mixtures

472

of chlorpyrifos and four other insecticides. Ecotoxicology 2014, 23, 221-228.

473

(29) Lv, S.; Zhang, K. Y.; Lin, Z. Z.; Tang, D. P. Novel photoelectrochemical

474

immunosensor for disease-related protein assisted by hemin/G-quadruplex-based

475

DNAzyme on gold nanoparticles to enhance cathodic photocurrent on p-CuBi2O4

476

semiconductor. Biosens. Bioelectron. 2017, 96, 317-323.

477

(30) Meher, H. C.; Gajbhiye, V. T.; Singh, G.; Kamra, A.; Chawla, G. Persistence and

478

Nematicidal Efficacy of Carbosulfan, Cadusafos, Phorate, and Triazophos in Soil and

479

Uptake by Chickpea and Tomato Crops under Tropical Conditions. J. Agr. Food. Chem.

480

2010, 58, 1815-1822.

481

(31) Xu, M. L.; Gao, Y.; Han, X. X.; Zhao, B. Detection of pesticide residues in food

482

using surface-enhanced Raman spectroscopy: A review. J. Agric. Food Chem. 2017, 65,

483

6719−6726.

484

(32) Liu, Y.; Zhou, H. B.; Hu, Z. W.; Yu, G. X; Yang, D. T; Zhao, J. S. Label and label-

485

free based surface-enhanced Raman scattering for pathogen bacteria detection: A

486

review. Biosens. Bioelectron. 2017, 94, 131–140.

487

(33) Zhao, F. N.; She, Y. X.; Zhang, C.; Cao, X. L.; Wang, S. S.; Zheng, L. F.; Jin, M. 22

ACS Paragon Plus Environment

Page 23 of 33

Journal of Agricultural and Food Chemistry

488

J.; Shao, H.; Jin, F.; Wang, J. Selective solid-phase extraction based on molecularly

489

imprinted technology for the simultaneous determination of 20 triazole pesticides in

490

cucumber samples using high-performance liquid chromatography-tandem mass

491

spectrometry. J. Chromatogr. B. 2017, 1064, 143-150.

492

(34) Zhang, J. J.; Sun, L.; Chen, C.; Liu, M.; Dong, W.; Guo, W. B.;. Ruan, S. P. High

493

performance humidity sensor based on metal organic framework MIL-101(Cr)

494

nanoparticles. J. Alloy. Compd. 2017, 695, 520-525.

495

(35) Hu, Y. L.; Liao, J.; Wang, D. M.; Li, G. K. Fabrication of Gold Nanoparticle-

496

Embedded Metal-Organic Framework for Highly Sensitive Surface-Enhanced Raman

497

Scattering Detection. Anal. Chem. 2014, 86, 3955-3963.

498

(36) Polsky, R.; Gill, R.; Kaganovsky, L.; Willner, I. Nucleic acid-functionalized Pt

499

nanoparticles: Catalytic labels for the amplified electrochemical detection of

500

biomolecules. Anal. Chem. 2006, 78, 2268-2271.

501

(37) Zhang, C.; Du, P. F.; Jiang, Z. J.; Jin, M. J.; Chen, G.; Cao, X. L.; Cui, X. Y.;

502

Zhang, Y. D.; Li, R. X.; Abd El-Aty, A. M.; Wang, J. A simple and sensitive

503

competitive bio-barcode immunoassay for triazophos based on multi-modified gold

504

nanoparticles and fluorescent signal amplification. Anal. Chim. Acta. 2018, 999, 123-

505

131.

506

(38) Guo, Y. R.; Liu, R.; Liu, Y.; Xiang, D. D.; Liu, Y. H.; Gui, W. J.; Li, M. Y.; Zhu,

507

G. N. A non-competitive surface plasmon resonance immunosensor for rapid detection

508

of triazophos residue in environmental and agricultural samples. Sci. Total. Environ.

509

2018, 613, 783-791. 23

ACS Paragon Plus Environment

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Page 24 of 33

510

(39) Liu, B. B.; Gong, H.; Wang, Y. L.; Zhang, X. S.; Li, P.; Qiu, Y. L.; Wang, L. M.;

511

Hua, X. D.; Guo, Y. R.; Wang, M. H.; Liu, F. Q.; Liu, X. J.; Zhang, C. Z. A gold

512

immunochromatographic assay for simultaneous detection of parathion and triazophos

513

in agricultural products. Anal. Methods-Uk. 2018, 10, 422-428.

514

(40) Boroduleva, A. Y.; Wu, J.; Yang, Q. Q.; Li, H.; Zhang, Q.; Li, P. W.; Eremin, S.

515

A. Development of fluorescence polarization immunoassays for parallel detection of

516

pesticides carbaryl and triazophos in wheat grains. Anal. Methods-Uk. 2017, 9, 6814-

517

6822.

518

(41) Xu, Z. L.; Wang, Q.; Lei, H. T.; Eremin, S. A.; Shen, Y. D.; Wang, H.; Beier, R.

519

C.; Yang, J. Y.; Maksimova, K. A.; Sun, Y. M. A simple, rapid and high-throughput

520

fluorescence

521

organophosphorus pesticides in vegetable and environmental water samples. Anal.

522

Chim. Acta. 2011, 708, 123-129.

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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.

530

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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