AU2021104855A4 - Molecularly imprinted polymer for detecting bacteria, and its preparation and use in bacterial detection - Google Patents

Molecularly imprinted polymer for detecting bacteria, and its preparation and use in bacterial detection Download PDF

Info

Publication number
AU2021104855A4
AU2021104855A4 AU2021104855A AU2021104855A AU2021104855A4 AU 2021104855 A4 AU2021104855 A4 AU 2021104855A4 AU 2021104855 A AU2021104855 A AU 2021104855A AU 2021104855 A AU2021104855 A AU 2021104855A AU 2021104855 A4 AU2021104855 A4 AU 2021104855A4
Authority
AU
Australia
Prior art keywords
electrodes
bacteria
molecularly imprinted
imprinted polymer
template
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Ceased
Application number
AU2021104855A
Inventor
Jikui WU
Junling Zhang
Min Zhu
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Shanghai Ocean University
Original Assignee
Shanghai Ocean University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Shanghai Ocean University filed Critical Shanghai Ocean University
Priority to AU2021104855A priority Critical patent/AU2021104855A4/en
Application granted granted Critical
Publication of AU2021104855A4 publication Critical patent/AU2021104855A4/en
Ceased legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N33/00Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
    • G01N33/48Biological material, e.g. blood, urine; Haemocytometers
    • G01N33/50Chemical analysis of biological material, e.g. blood, urine; Testing involving biospecific ligand binding methods; Immunological testing
    • G01N33/53Immunoassay; Biospecific binding assay; Materials therefor
    • G01N33/569Immunoassay; Biospecific binding assay; Materials therefor for microorganisms, e.g. protozoa, bacteria, viruses
    • G01N33/56911Bacteria
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12QMEASURING OR TESTING PROCESSES INVOLVING ENZYMES, NUCLEIC ACIDS OR MICROORGANISMS; COMPOSITIONS OR TEST PAPERS THEREFOR; PROCESSES OF PREPARING SUCH COMPOSITIONS; CONDITION-RESPONSIVE CONTROL IN MICROBIOLOGICAL OR ENZYMOLOGICAL PROCESSES
    • C12Q1/00Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions
    • C12Q1/02Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions involving viable microorganisms
    • C12Q1/04Determining presence or kind of microorganism; Use of selective media for testing antibiotics or bacteriocides; Compositions containing a chemical indicator therefor
    • C12Q1/06Quantitative determination
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12QMEASURING OR TESTING PROCESSES INVOLVING ENZYMES, NUCLEIC ACIDS OR MICROORGANISMS; COMPOSITIONS OR TEST PAPERS THEREFOR; PROCESSES OF PREPARING SUCH COMPOSITIONS; CONDITION-RESPONSIVE CONTROL IN MICROBIOLOGICAL OR ENZYMOLOGICAL PROCESSES
    • C12Q1/00Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions
    • C12Q1/02Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions involving viable microorganisms
    • C12Q1/04Determining presence or kind of microorganism; Use of selective media for testing antibiotics or bacteriocides; Compositions containing a chemical indicator therefor
    • C12Q1/10Enterobacteria
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12QMEASURING OR TESTING PROCESSES INVOLVING ENZYMES, NUCLEIC ACIDS OR MICROORGANISMS; COMPOSITIONS OR TEST PAPERS THEREFOR; PROCESSES OF PREPARING SUCH COMPOSITIONS; CONDITION-RESPONSIVE CONTROL IN MICROBIOLOGICAL OR ENZYMOLOGICAL PROCESSES
    • C12Q1/00Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions
    • C12Q1/02Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions involving viable microorganisms
    • C12Q1/04Determining presence or kind of microorganism; Use of selective media for testing antibiotics or bacteriocides; Compositions containing a chemical indicator therefor
    • C12Q1/14Streptococcus; Staphylococcus
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N33/00Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
    • G01N33/48Biological material, e.g. blood, urine; Haemocytometers
    • G01N33/483Physical analysis of biological material
    • G01N33/487Physical analysis of biological material of liquid biological material
    • G01N33/48707Physical analysis of biological material of liquid biological material by electrical means
    • G01N33/48735Investigating suspensions of cells, e.g. measuring microbe concentration
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N33/00Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
    • G01N33/48Biological material, e.g. blood, urine; Haemocytometers
    • G01N33/50Chemical analysis of biological material, e.g. blood, urine; Testing involving biospecific ligand binding methods; Immunological testing
    • G01N33/53Immunoassay; Biospecific binding assay; Materials therefor
    • G01N33/543Immunoassay; Biospecific binding assay; Materials therefor with an insoluble carrier for immobilising immunochemicals
    • G01N33/54366Apparatus specially adapted for solid-phase testing
    • G01N33/54373Apparatus specially adapted for solid-phase testing involving physiochemical end-point determination, e.g. wave-guides, FETS, gratings
    • G01N33/5438Electrodes
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N33/00Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
    • G01N33/48Biological material, e.g. blood, urine; Haemocytometers
    • G01N33/50Chemical analysis of biological material, e.g. blood, urine; Testing involving biospecific ligand binding methods; Immunological testing
    • G01N33/53Immunoassay; Biospecific binding assay; Materials therefor
    • G01N33/543Immunoassay; Biospecific binding assay; Materials therefor with an insoluble carrier for immobilising immunochemicals
    • G01N33/54393Improving reaction conditions or stability, e.g. by coating or irradiation of surface, by reduction of non-specific binding, by promotion of specific binding
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N33/00Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
    • G01N33/48Biological material, e.g. blood, urine; Haemocytometers
    • G01N33/50Chemical analysis of biological material, e.g. blood, urine; Testing involving biospecific ligand binding methods; Immunological testing
    • G01N33/53Immunoassay; Biospecific binding assay; Materials therefor
    • G01N33/569Immunoassay; Biospecific binding assay; Materials therefor for microorganisms, e.g. protozoa, bacteria, viruses
    • G01N33/56911Bacteria
    • G01N33/56916Enterobacteria, e.g. shigella, salmonella, klebsiella, serratia
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N33/00Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
    • G01N33/48Biological material, e.g. blood, urine; Haemocytometers
    • G01N33/50Chemical analysis of biological material, e.g. blood, urine; Testing involving biospecific ligand binding methods; Immunological testing
    • G01N33/53Immunoassay; Biospecific binding assay; Materials therefor
    • G01N33/569Immunoassay; Biospecific binding assay; Materials therefor for microorganisms, e.g. protozoa, bacteria, viruses
    • G01N33/56911Bacteria
    • G01N33/56938Staphylococcus
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N27/00Investigating or analysing materials by the use of electric, electrochemical, or magnetic means
    • G01N27/26Investigating or analysing materials by the use of electric, electrochemical, or magnetic means by investigating electrochemical variables; by using electrolysis or electrophoresis
    • G01N27/28Electrolytic cell components
    • G01N27/30Electrodes, e.g. test electrodes; Half-cells
    • G01N27/327Biochemical electrodes, e.g. electrical or mechanical details for in vitro measurements
    • G01N27/3275Sensing specific biomolecules, e.g. nucleic acid strands, based on an electrode surface reaction
    • G01N27/3277Sensing specific biomolecules, e.g. nucleic acid strands, based on an electrode surface reaction being a redox reaction, e.g. detection by cyclic voltammetry
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/30Against vector-borne diseases, e.g. mosquito-borne, fly-borne, tick-borne or waterborne diseases whose impact is exacerbated by climate change

Landscapes

  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Immunology (AREA)
  • Molecular Biology (AREA)
  • Biomedical Technology (AREA)
  • Hematology (AREA)
  • Urology & Nephrology (AREA)
  • Physics & Mathematics (AREA)
  • General Health & Medical Sciences (AREA)
  • Organic Chemistry (AREA)
  • Biochemistry (AREA)
  • Analytical Chemistry (AREA)
  • Microbiology (AREA)
  • Biotechnology (AREA)
  • Wood Science & Technology (AREA)
  • Pathology (AREA)
  • Proteomics, Peptides & Aminoacids (AREA)
  • Zoology (AREA)
  • Medicinal Chemistry (AREA)
  • Food Science & Technology (AREA)
  • General Physics & Mathematics (AREA)
  • Cell Biology (AREA)
  • Biophysics (AREA)
  • Tropical Medicine & Parasitology (AREA)
  • Toxicology (AREA)
  • Virology (AREA)
  • Bioinformatics & Cheminformatics (AREA)
  • General Engineering & Computer Science (AREA)
  • Genetics & Genomics (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Measuring Or Testing Involving Enzymes Or Micro-Organisms (AREA)

Abstract

(FIG. 1) The present disclosure is related to the field of biochemistry, and in particular, to a molecularly imprinted polymer for detecting bacteria and its preparation and use in bacterial detection. A method for preparation of a molecularly imprinted polymer for detecting bacteria comprises: (a) adding bacteria serving as a template molecular that is used for imprinting, a functional monomer, and a dopant to a buffer solution at a predetermined ratio to form a mixed liquid, into which electrodes are immersed to conduct an electrochemical polymerization reaction so as to form a conducting polymer on surfaces of the electrodes; and (b) placing the electrodes having the conducting polymer formed thereon in an elution solution to remove the template bacteria, followed by drying of the electrodes with a protective gas, so as to obtain a molecularly imprinted polymer for detecting the bacteria on the surfaces of the electrodes. By combining the mechanism of effective improvement of PPy conductivity by CuPcTs with the mechanism of specific recognition of the template bacteria by a molecularly imprinted polymer, a molecularly imprinted polymer is provided which has good capability for recognizing a target bacteria species with high sensitivity and specificity. -1/4 8 CsPyC~~-I+.cl 6- GCEs/PPy-CuPcTs-MIP+ci * CsP4-uc--I ME6OEO MMM N 2- ~m MuU 00 60 A' 5 50B 90.0 60- 60 20 90 60 30 0.05 0.10 01')5 0.20 025 5 to Is 20 Cu~cTsIC (mmol/nL) Electropolymerization C 500 D01o0 400- 80 300- 60 C: 200- 40 100 20 0 04 0.5 1.0 1.5 2.0 1.0 1.5 2.0 2.5 Template Removal Time h Recognition Time/h FIG.2

Description

-1/4
8 CsPyC~~-I+.cl
6- GCEs/PPy-CuPcTs-MIP+ci
* CsP4-uc--I MMM ME6OEO
N 2- ~m MuU
00
60
A' 5 50B 90.0
60- 60
20 90
60 30
0.05 0.10 01')5 0.20 025 5 to Is 20
Cu~cTsIC (mmol/nL) Electropolymerization C500 D01o0
400- 80
300- 60 C:
200- 40
20
100
0 04 0.5 1.0 1.5 2.0 1.0 1.5 2.0 2.5 Template Removal Time h Recognition Time/h
FIG.2
MOLECULARLY IMPRINTED POLYMER FOR DETECTING BACTERIA, AND ITS PREPARATION AND USE IN BACTERIAL DETECTION TECHNICAL FIELD
[01] The present disclosure is related to the field of biochemistry, and in particular, to a molecularly imprinted polymer for detecting bacteria, and its preparation and use in bacterial
detection.
BACKGROUNDART
[02] Standards for pathogen limits for food are integral to food safety standards, and
National Food Safety Standard - Pathogen Limits for Food is the first standard that specifies the
limits of pathogens in food. In particular, this standard specifies the limits of the most common
kinds of pathological bacteria, including Salmonella, Staphylococcus aureus (S. aureus), Vibrio
Parahemolyticus (VP), Listeria monocytogenes (L. monocytogenes), and Escherichia coli (E.
coli), in foods including meat products, aquatic products, grain products, ready-to-eat fruit and
vegetable products, beverages, and frozen drinks. According to this standard, the limits of
csalmonella and Staphylococcus aureus in the foods are zero and 100 CFU/g, respectively.
[03] Conventional techniques for bacterial detection, such as enzyme-linked immunosorbent
assay (ELISA), radioimmunoassay (RIA), and real-time quantitative polymerase chain reaction
(qPCR), suffer from a number of disadvantages, such as very slow response speed, complex
sample preparation, bulky and expensive devices, and limited sensitivity and selectivity.
Therefore, it is of great importance for public health and food safety to provide a faster, less
costly, and more sensitive and specific method for detecting pathogens.
SUMMARY
[04] In view of the above problems, embodiments of the present disclosure provide a
molecularly imprinted polymer for detecting bacteria and a method for preparation thereof, as
well as a method for detecting bacteria by using the molecularly imprinted polymer with high
sensitivity and specificity.
[05] Accordingly, one embodiment provides a method for preparation of a molecularly imprinted polymer for detecting bacteria, comprising steps of:
[06] (a) adding bacteria serving as a target molecular or a template that is used for imprinting (hereinafter also referred to as the template bacteria), a functional monomer, and a
dopant to a buffer solution at a predetermined ratio to form a mixed liquid, into which
electrodes are immersed to conduct an electrochemical polymerization reaction so as to form a
conducting polymer on surfaces of the electrodes; and
[07] (b) placing the electrodes having the conducting polymer formed thereon in an elution
solution to remove the template bacteria, followed by drying of the electrodes with a protective
gas, so as to obtain a molecularly imprinted polymer for detecting the bacteria on the surfaces
of the electrodes.
[08] The template bacteria may be Listeria monocytogenes (L. monocytogenes),
Staphylococcus aureus (S. aureus), Salmonella, or Escherichia coli 0157:H7 (E. coli 0157:H7)
species.
[09] The dopant may be copper tetrasulfonatophthalocyanine (CuPcTs).
[10] The functional monomer may be pyrrole.
[11] The predetermined ratio of the template bacteria, the functional monomer, and the
dopant may be 500:17:(0.05-0.25) by volume, preferably 500:17:0.1 by volume.
[12] The buffer solution may be a 0.1 mol/L potassium chloride solution containing 1 mmol/L potassium ferricyanide (K3[Fe(CN) 6]) and 1 mmol/L potassium hexacyanoferrate(II)
(K4Fe(CN) 6).
[13] The electrochemical polymerization reaction in the step (a) may be conducted via cyclic
voltammetry. In particular, when the electrodes are immersed in the mixed liquid containing the
template bacteria, the functional monomer, and the dopant, scan parameters and the number of
electropolymerization cycles are set to predetermined values so as to carry out the
electrochemical polymerization reaction in the buffer solution.
[14] Further, the scan parameters may include a scan rate and a circulation voltage, which may be set to 0.05 V/s and - 0.4 to +0.7 V, respectively. The number of electropolymerization cycles may be set to 5 to 20, preferably 15. The polymerization reaction may be conducted at room temperature.
[15] The elution solution used in the step (b) may be an acetic acid solution containing 5
% by weight of sodium dodecyl sulfate (SDS).
[16] The electrodes used in the step (a) may be glassy carbon electrodes, which may be pretreated by grinding and polishing surfaces of the electrodes using a suspension of aluminium oxide particles having a particle size of 0.05 to 0.3 m and subjecting the electrodes to ultrasonic cleaning using deionized water for 30 seconds to 1 minute and then using an organic solvent, such as ethanol or acetone, for a further 30 seconds to 1 minute, followed by drying with a protective gas.
[17] Another embodiment provides a molecularly imprinted polymer for detecting bacteria prepared according to the method as described above.
[18] A further embodiment provides a method for detecting bacteria, comprising:
[19] detecting bacteria in a sample by using the molecularly imprinted polymer as described above, and measuring impedance via electrochemical impedance spectroscopy (EIS) measurement to determine recovery of the bacteria.
[20] The EIS measurement may be performed at room temperature with a frequency of 0.1 to 100,000 Hz and an amplitude of 5 mV.
[21] The bacteria in the sample may be L. monocytogenes, S. aureus, Salmonella, or E. coli 0157:H7 species.
[22] The electrochemical polymerization can enable the thickness of the conducting polymer film to be controlled and thus a uniform surface imprinting layer to be formed on the electrodes, and also enable the surface imprinting layer to be securely bound to the electrodes. Polypyrrole (PPy) is known to have low nonspecific adsorption ability, good conductivity, and excellent stability, and can be readily formed by polymerization of pyrrole monomers at mild conditions in an efficient manner. Furthermore, PPy has sensitivity to active sites on the outside of the bacterial cells, and thus has high selectivity and versatility for various bacteria.
[23] We have experimentally found that the use of CuPcTs (which is a conductive supramolecular material) as a dopant in the preparation of the molecularly imprinted polymer
can further improve the sensitivity and the specificity of the molecularly imprinted polymer to
the template bacteria. CuPcTs is known as a good organic semiconductor material, and we have
also found that the conductivity of PPy doped with CuPcTs is two orders of magnitude higher
than pure (undoped) PPy, that is, the conductivity of PPy doped with CuPcTs is substantially
increased.
[24] We therefore use pyrrole as the functional monomer. As such, the mechanism of
effective improvement of PPy conductivity by CuPcTs can be combined with the mechanism of
specific recognition of the template bacteria by the molecularly imprinted polymer. In this way,
the molecularly imprinted polymer prepared may have a higher selectivity for a target
molecular, and the sensitivity and accuracy of bacteria detection by using such molecularly
imprinted polymer can be improved.
[25] The present disclosure provides several advantages over prior art. By combining the mechanism of effective improvement of PPy conductivity by CuPcTs with the mechanism of
specific recognition of the template bacteria by a molecularly imprinted polymer, a molecularly
imprinted polymer is provided which has good capability for recognizing a target molecular
with high sensitivity and specificity. The method for preparation of the molecularly imprinted
polymer according to the present disclosure is commercially feasible, rapid, simple, and
efficient. Further, the molecularly imprinted polymer of the present disclosure can be used to
detect bacteria with high sensitivity and specificity.
[26] Definitions of specific embodiments of the present disclosure as claimed herein follow.
[27] According to a first specific embodiment, there is provided a method for preparation of
a molecularly imprinted polymer for detecting bacteria, comprising steps of:
(a) adding bacteria serving as a template molecular that is used for imprinting, a
functional monomer, and a dopant to a buffer solution at a predetermined ratio to form a mixed
liquid, into which electrodes are immersed to conduct an electrochemical polymerization
reaction so as to form a conducting polymer on surfaces of the electrodes; and
(b) placing the electrodes having the conducting polymer formed thereon in an elution
solution to remove the template bacteria, followed by drying of the electrodes with a protective
gas, so as to obtain a molecularly imprinted polymer for detecting the bacteria on the surfaces
of the electrodes;
wherein the template bacteria is Listeria monocytogenes, Staphylococcus aureus,
Salmonella, or Escherichia coli 0157:H7 species;
the dopant is copper tetrasulfonatophthalocyanine; and
the functional monomer is pyrrole.
[28] According to a second specific embodiment, there is provided a molecularly imprinted
polymer prepared according to the method of the first aspect.
[29] The term "comprise" and variants of the term such as "comprises" or "comprising" are used herein to denote the inclusion of a stated integer or stated integers but not to exclude any
other integer or any other integers, unless in the context of usage an exclusive interpretation of
the term is required.
BRIEF DESCRIPTION OF THE DRAWINGS
[30] FIG. 1 is a graph showing electrochemical impedance spectroscopy (EIS) data for
GCEs/PPy-CuPcTs-MIP immersed in a 0.1 mol/L KCl solution containing 1 mmol/L
K3[Fe(CN) 6] and 1 mmol/L K 4 Fe(CN) 6 and EIS data for GCEs/PPy-CuPcTs-MIP immersed in a
0.1 mol/L KCl solution containing 1 mmol/L K3[Fe(CN) 6] and 1 mmol/L K 4 Fe(CN) 6 after
recognitionof anE. coli0157:H7 species;
[31] FIG. 2 shows optimization of parameters including (A) concentration of CuPcTs, (B)
polymerization cycles, (C) template removal time, and (D) recognition time;
[32] FIG. 3A shows the impedance spectra of GCEs/PPy-CuPcTs-MIP for detection of E.
coli 0157:H7 at series of gradient concentrations from 10 to 108 CFU/mL;
[33] FIG. 3B shows the standard curve of the EIS response versus log concentration of E. coli 0157:H7;
[34] FIG. 4 shows the EIS response of different biosensors of GCEs/PPy-CuPcTs-MIP to the respective template bacteria and the other three interfering bacteria species; and
[35] FIG. 5 is a graph showing EIS data for GCEs/bare, GCEs/PPy, and GCEs/PPy-CuPcTs immersed in a 0.1 mol/L KCl solution containing 1 mmol/L K3[Fe(CN) 6] and 1 mmol/L K 4Fe(CN) 6 .
DETAILED DESCRIPTION OF THE EMBODIMENTS
[36] The molecularly imprinted polymer (which was actually formed on the surfaces of the electrodes) used in the following examples 1 to 10 was prepared as follows.
[37] Surfaces of glassy carbon electrodes were ground and polished with a suspension of aluminium oxide particles having a particle size of 0.05 to 0.3 m. Thereafter, the electrodes were ultrasonically cleaned in deionized water and ethanol each for 30 s, and then dried with nitrogen. 17 L of pyrrole (functional monomer), 0.1 L of CuPcTs (dopant), 0.5 mL of a solution containing an E. coli 0157:H7 concentration of 106 CFU/mL (template bacteria), and 4 mL of a buffer solution (that is a 0.1 mol/L KCl solution containing1 mmol/L K3[Fe(CN) 6] and 1 mmol/L K4 Fe(CN) 6) were well mixed and introduced into a 5 mL-beaker. The glassy carbon electrodes were then immersed in the mixed liquid in the beaker to conduct electrochemical polymerization at room temperature via cyclic voltammetry under the conditions of a scan rate of 0.05 V/s, a cyclic voltage of from -0.4 V to +0.7 V, and 15 electropolymerization cycles. After completion of the polymerization, the electrodes were removed from the beaker and rinsed several times with deionized water and then dried with nitrogen. Then, the electrodes were subjected to elution with SDS/HAc (5 % w/v) for 1.5 h to remove the template bacteria, and were rinsed several times with deionized water and then dried with nitrogen. A molecularly imprinted polymer was thus obtained on the surfaces of the electrodes (such electrodes are also referred to herein as the modified electrodes or the biosensor GCEs/PPy-CuPcTs-MIP).
[38] Example 1
[39] 9 mL of drinking water was well mixed with 1 mL of phosphate buffered saline (PBS, pH=7.4) containing E. coli 0157:H7 to prepare artificially contaminated samples having
concentrations of 10', 104, and 105 CFU/mL, respectively. A volume of 250 L of each sample
was transferred into a 1-mL centrifuge tube. The modified electrodes were immersed in each
sample solution for 2 h, and EIS measurement was then performed thereon. The specificity of
the molecularly imprinted polymer formed on the surfaces of the electrodes to E. coli 0157:H7
and recovery of E. coli 0157:H7 were investigated. The results are shown in Table 1.
[40] Example 2
[41] 9 mL of orange juice was well mixed with 1 mL of PBS (pH=7.4) containing E. coli 0157:H7 to prepare artificially contaminated samples having concentrations of 103, 104,
and 105 CFU/mL, respectively. A volume of 250 L of each sample was transferred into a 1-mL
centrifuge tube. The modified electrodes were immersed in each sample solution for 2 h, and
EIS measurement was then performed thereon. The specificity of the molecularly imprinted
polymer formed on the surfaces of the electrodes to E. coli 0157:H7 and recovery of E.
coli 0157:H7 were investigated. The results are shown in Table 1.
[42] Example 3
[43] Some constituents of milk, such as lipids and proteins, may interfere with detection of
bacteria, so the milk to be used was centrifuged and filtered before use. In particular, the milk
was centrifuged to give a supernatant, which was filtered through a sterile microporous
membrane. 9 mL of the filtered supernatant was well mixed with 1 mL of PBS (pH=7.4)
containing E. coli 0157:H7 to prepare artificially contaminated samples having concentrations
of 103, 104, and 105 CFU/mL, respectively. A volume of 250 L of each sample was transferred into a 1-mL centrifuge tube. The modified electrodes were immersed in each sample solution
for 2 h, and EIS measurement was then performed thereon. The specificity of the molecularly
imprinted polymer formed on the surfaces of the electrodes to E. coli 0157:H7 and recovery of
E. 0157:H7 were investigated. The results are shown in Table 1.
[44] Table1 Detection ofE. coli 0157:H7 in the Samples Added Measured Recovery RSD /(CFU/mL) /(CFU/mL) /% /(%, n=3)
103 9.81x102 98.1 2.49
Example 1 104 9.79x103 97.9 1.10
105 1.008x105 100.8 3.37
103 1.026x103 102.6 1.21
Example 2 104 9.07x 103 90.7 3.53
105 1.01x105 101.0 1.43
103 9.61x102 96.1 2.35
Example 3 104 9.53x103 95.3 1.52 105 1.022x105 102.0 2.30
[45] The contents of E. coli 0157:H7 in the samples were determined by using the biosensor GCEs/PPy-CuPcTs-MIP. The recovery of E. coli 0157:H7 in drinking water was 97.9 to 100.8
% with a relative standard deviation (RSD) of from 1.10 to 3.37 %; the recovery of E. coli 0157:H7 in orange juice was 90.7 to 102.6 % with RSD of from 1.21 to 3.53 %; and the
recovery of E. coli 0157:H7 in milk was 95.3 to 102.2 % with RSD of from 1.52 to 2.35 %, as
shown in Table 1. These indicate that the biosensor GCEs/PPy-CuPcTs-MIP is suitable for detecting E. coli 0157:H7 in real samples.
[46] Example 4
[47] The modified electrodes were immersed in a buffer solution (that is a 0.1 mol/L potassium chloride solution containing 1 mmol/L K3[Fe(CN) 6 ] and 1 mmol/L K4Fe(CN) 6), and EIS measurement was then performed thereon. The results are shown in FIG. 1.
[48] Surfaces of glassy carbon electrodes were ground and polished with a suspension of aluminium oxide particles having a particle size of 0.05 to 0.3 m. Thereafter, the electrodes were ultrasonically cleaned in deionized water and ethanol each for 30 s, and then dried with nitrogen. 17 L of pyrrole (functional monomer), 0.1 L of CuPcTs (dopant), 0.5 mL of a solution containing an E. coli 0157:H7 concentration of 106 CFU/mL (template bacteria), and 4 mL of a buffer solution (that is a 0.1 mol/L KCl solution containing1 mmol/L K3[Fe(CN) 6] and 1 mmol/L K4 Fe(CN) 6) were well mixed and introduced into a 5 mL-beaker. The glassy carbon electrodes were then immersed in the mixed liquid in the beaker to conduct electrochemical polymerization at room temperature via cyclic voltammetry under the conditions of a scan rate of 0.05 V/s, a cyclic voltage of from -0.4 V to +0.7 V, and 15 electropolymerization cycles. After completion of the polymerization, the electrodes were removed from the beaker and rinsed several times with deionized water and then dried with nitrogen. Then, the electrodes were subjected to elution with SDS/HAc (5 % w/v) for 1.5 h to remove the template bacteria, and were rinsed several times with deionized water and then dried with nitrogen. A molecularly imprinted polymer was thus obtained on the surfaces of the electrodes.
[49] A volume of 250 L of a solution containing an E. coli 0157:H7 concentration of 106 CFU/mL was introduced into a 1-mL centrifuge tube. The modified electrodes were immersed in the solution in the tube for 2 h for recognition of E. coli 0157:H7, and EIS measurement was then performed thereon. The measurement results are shown in FIG. 1.
[50] FIG. 1 is a graph showing EIS data for the biosensor GCEs/PPy-CuPcTs-MIP immersed in the buffer solution and EIS data for the biosensor GCEs/PPy-CuPcTs-MIP immersed in the buffer solution after recognition of E. coli 0157:H7 (106 CFU/mL). It can be seen from this figure that, after recognition of E. coli0157:H7 (106 CFU/mL), the biosensor GCEs/PPy-CuPcTs-MIP had an impedance of 9,000 Q, which was considerably higher than that of the biosensor GCEs/PPy-CuPcTs-MIP before the recognition, which was 50 Q.
[51] Example 5
[52] A volume of 250 L of a solution containing an E. coli 0157:H7 concentration of 106 CFU/mL was introduced into a 1-mL centrifuge tube. The modified electrodes were immersed in the solution in the tube for 2 h for recognition of E. coli 0157:H7, and EIS measurement was then performed thereon. The measurement results are shown in FIG. 2. It can be seen from FIG. 2 that, the sensing performance of the biosensor GCEs/PPy-CuPcTs-MIP was gradually improved as the concentration of CuPcTs was increased from 0.05 to 0.10 mol/L; while, when the concentration of CuPcTs was further increased to 0.15 to 0.25 mol/L, its reactivity to the template bacteria was reduced. The optimal concentration of CuPcTs was thus determined to be
0.10 mol/L.
[53] Example 6
[54] A volume of 250 L of a solution containing an E. coli 0157:H7 concentration of 106
CFU/mL was introduced into a 1-mL centrifuge tube. The modified electrodes were immersed
in the solution in the tube for 2 h for recognition of E. coli 0157:H7, and EIS measurement was
then performed thereon. The measurement results are shown in FIG. 2. It can be seen from FIG.
2 that the sensing performance of the biosensor GCEs/PPy-CuPcTs-MIP was gradually
improved as the number of the polymerization cycles were increased from 5 to 15; while, when
the number of the polymerization cycles was further increased to 20, its reactivity to the
template bacteria was reduced. The optimal number of polymerization cycles was thus
determined to be 15.
[55] Example 7
[56] A volume of 250 L of a solution containing an E. coli 0157:H7 concentration of 106
CFU/mL was introduced into a 1-mL centrifuge tube. The modified electrodes were immersed
in the solution in the tube for 2 h for recognition of E. coli 0157:H7, and EIS measurement was
then performed thereon. The measurement results are shown in FIG. 2. It can be seen from FIG.
2 that the elution time could influence the removal of the template bacteria. In particular, the Ret
value was decreased as the elution time was increased from 0.5 to 1.5 h; while, when the elution
time was further increased to 2 h, the Rt value did not vary any longer. The optimal elution
time was thus determined to be 1.5 h.
[57] Example 8
[58] A volume of 250 L of a solution containing an E. coli 0157:H7 concentration of 106
CFU/mL was introduced into a 1-mL centrifuge tube. The modified electrodes were immersed
in the solution in the tube for 1 to 2.5 h for recognition of E. coli0157:H7, and EIS
measurement was then performed thereon. The measurement results are shown in FIG. 2. It can be seen from FIG. 2 that the recognition time is a further parameter that may influence the sensing performance of the sensor. In particular, the intensity of the response signal was gradually increased as the recognition time was increased from 1 to 2 h; while, when the recognition time was further increased to 2.5 h, the intensity of the response signal did not vary significantly any longer. The optimum recognition time was thus determined to be 2 h.
[59] Example 9 - Establishment of Standard Curve
[60] A solution containing E. coli 0157:H7 was diluted with PBS (pH=7.4) by 10-fold serial dilution to prepare standard samples having concentrations of 10, 102, 10 , 104, 105, 106, 107,
and 108 CFU/mL, respectively. A volume of 250 L of each standard sample was introduced
into a 1-mL centrifuge tube. The modified electrodes were immersed in the solution in the tube
for 2 h for recognition of E. coli 0157:H7, and EIS measurement was then performed thereon.
[61] A standard curve was established based on the EIS response of the biosensor
GCEs/PPy-CuPcTs-MIP at different concentrations of E. coli0157:H7. FIG. 3A shows the
impedance spectra of GCEs/PPy-CuPcTs-MIP for detection of E. coli 0157:H7 at series of
gradient concentrations from 10 to 108 CFU/mL; and FIG. 3B shows the standard curve of the
EIS response versus log concentration of E. coli 0157:H7. The standard curve was linear in the
range of 10 to 108 CFU/mL, and the equation was: AR/R(Q)=10.83logioC - 9.40, with a
correlation coefficient R 2 =0.9938. The minimum detection limit was 10 CFU/mL. In order to
accurately determine the concentration of E. coli 0157:H7 in a sample, the concentration of E.
coli0157:H7 in the sample should not exceed 108 CFU/mL. If the concentration of E.
coli 0157:H7 in a sample is not within such range, the sample may be diluted or concentrated.
[62] Example 10
[63] 250 L of each of solutions containing E. coli 0157:H7, L. monocytogenes, S. aureus,
and Salmonella, respectively, at a concentration of 106 CFU/mL, were introduced into a 1-mL
centrifuge tube. The modified electrodes were immersed in the solution in each tube for 2 h for
recognition of the respective bacteria species, and EIS measurement was then performed
thereon. The measurement results are shown in FIG. 4.
[64] Example 11
[65] Surfaces of glassy carbon electrodes were ground and polished with a suspension of aluminium oxide particles having a particle size of 0.05 to 0.3 m. Thereafter, the electrodes
were ultrasonically cleaned in deionized water and ethanol each for 30 s, and then dried with
nitrogen. 17 L of pyrrole (functional monomer), 0.1 L of CuPcTs (dopant), 0.5 mL of a
solution containing a L. monocytogenes concentration of 106 CFU/mL (template bacteria), and
4 mL of a buffer solution (that is a 0.1 mol/L potassium chloride solution containing 1 mmol/L
K3[Fe(CN) 6] and 1 mmol/L K 4 Fe(CN) 6) were well mixed and introduced into a 5 mL-beaker.
The glassy carbon electrodes were then immersed in the mixed liquid in the beaker to conduct
electrochemical polymerization at room temperature via cyclic voltammetry under the
conditions of a scan rate of 0.05 V/s, a cyclic voltage of from -0.4 V to +0.7 V, and 15
electropolymerization cycles. After completion of the polymerization, the electrodes were
removed from the beaker and rinsed several times with deionized water and then dried with
nitrogen. Then, the electrodes were subjected to elution with SDS/HAc (5 % w/v) for 1.5 h to
remove the template bacteria, and rinsed several times with deionized water and then dried with
nitrogen. A molecularly imprinted polymer was thus obtained on the surfaces of the electrodes.
[66] 250 L of each of solutions containing E. coli 0157:H7, L. monocytogenes, S. aureus, and Salmonella, respectively, at a concentration of 106 CFU/mL, were introduced into a 1-mL
centrifuge tube. The modified electrodes were immersed in the solution in each tube for 2 h for
recognition of the respective bacteria species, and EIS measurement was then performed
thereon. The measurement results are shown in FIG. 4.
[67] Example 12
[68] Surfaces of glassy carbon electrodes were ground and polished with a suspension of
aluminium oxide particles having a particle size of 0.05 to 0.3 m. Thereafter, the electrodes
were ultrasonically cleaned in deionized water and ethanol each for 30 s, and then dried with
nitrogen. 17 L of pyrrole (functional monomer), 0.1 L of CuPcTs (dopant), 0.5 mL of a
solution containing a S. aureus concentration of 106 CFU/mL (template bacteria), and 4 mL of a
buffer solution (that is a 0.1 mol/L potassium chloride solution containing 1 mmol/L
K3[Fe(CN) 6] and 1 mmol/L K 4 Fe(CN) 6) were well mixed and introduced into a 5 mL-beaker.
The glassy carbon electrodes were then immersed in the mixed liquid in the beaker to conduct electrochemical polymerization at room temperature via cyclic voltammetry under the conditions of a scan rate of 0.05 V/s, a cyclic voltage of from -0.4 V to +0.7 V, and 15 electropolymerization cycles. After completion of the polymerization, the electrodes were removed from the beaker and rinsed several times with deionized water and then dried with nitrogen. Then, the electrodes were subjected to elution with SDS/HAc (5 % w/v) for 1.5 h to remove the template bacteria, and rinsed several times with deionized water and then dried with nitrogen. A molecularly imprinted polymer was thus obtained on the surfaces of the electrodes.
[69] 250 L of each of solutions containing E. coli 0157:H7, L. monocytogenes, S. aureus, and Salmonella, respectively, at a concentration of 106 CFU/mL, were introduced into a 1-mL centrifuge tube. The modified electrodes were immersed in the solution in each tube for 2 h for recognition of the respective bacteria species, and EIS measurement was then performed thereon. The measurement results are shown in FIG. 4.
[70] Example 13
[71] Surfaces of glassy carbon electrodes were ground and polished with a suspension of aluminium oxide particles having a particle size of 0.05 to 0.3 m. Thereafter, the electrodes were ultrasonically cleaned in deionized water and ethanol each for 30 s, and then dried with nitrogen. 17 L of pyrrole (functional monomer), 0.1 L of CuPcTs (dopant), 0.5 mL of a solution containing a Salmonella concentration of 106 CFU/mL (template bacteria), and 4 mL of a buffer solution (that is a 0.1 mol/L potassium chloride solution containing 1 mmol/L K3[Fe(CN) 6] and 1 mmol/L K 4 Fe(CN) 6) were well mixed and introduced into a 5 mL-beaker.
The glassy carbon electrodes were then immersed in the mixed liquid in the beaker to conduct electrochemical polymerization at room temperature via cyclic voltammetry under the conditions of a scan rate of 0.05 V/s, a cyclic voltage of from -0.4 V to +0.7 V, and 15 electropolymerization cycles. After completion of the polymerization, the electrodes were removed from the beaker and rinsed several times with deionized water and then dried with nitrogen. Then, the electrodes were subjected to elution with SDS/HAc (5 % w/v) for 1.5 h to remove the template bacteria, and rinsed several times with deionized water and then dried with nitrogen. A molecularly imprinted polymer was thus obtained on the surfaces of the electrodes.
[72] 250 L of each of solutions containing E. coli 0157:H7, L. monocytogenes, S. aureus, and Salmonella, respectively, at a concentration of 106 CFU/mL, were introduced into a 1-mL
centrifuge tube. The modified electrodes were immersed in the solution in each tube for 2 h for
recognition of the respective bacteria species, and EIS measurement was then performed
thereon. The measurement results are shown in FIG. 4.
[73] FIG. 4 shows EIS response of the different biosensors of GCEs/PPy-CuPcTs-MIP to the
respective template bacteria and the other three interfering bacteria species. It can be seen from
this figure that in the case of the template bacteria of E. coli 0157:H7, the EIS response of the
biosensors to E. coli 0157:H7 was higher than the response to the other interfering bacteria
species. Similarly, in the cases that the template bacteria was L. monocytogenes, S. aureus, or
Salmonella, the EIS response of the biosensors to the template bacteria was also higher than the
response to the other interfering bacteria species. Thus, the biosensor GCEs/PPy-CuPcTs-MIP
had high selectivity and versatility for the various bacteria speciess.
[74] Comparative Example 1
[75] Surfaces of glassy carbon electrodes (GCEs) were ground and polished with a
suspension of aluminium oxide particles having a particle size of 0.05 to 0.3 [m. Thereafter, the
electrodes were ultrasonically cleaned in deionized water and ethanol each for 30 s. The
electrodes so obtained was referred to as GCEs/bare herein. The GCEs/bare were then
immersed in a buffer solution, that is a 0.1 mol/L potassium chloride solution containing 1
mmol/L K3[Fe(CN) 6 ] and 1 mmol/L K 4 Fe(CN) 6, and EIS measurement was then performed
thereon.
[76] Comparative Example 2
[77] Surfaces of glassy carbon electrodes were ground and polished with a suspension of
aluminium oxide particles having a particle size of 0.05 to 0.3 m. Thereafter, the electrodes
were ultrasonically cleaned in deionized water and ethanol each for 30 s, and then dried with nitrogen. 17 L of pyrrole (functional monomer) and 4 mL of a buffer solution (that is a 0.1 mol/L potassium chloride solution containing 1 mmol/L K3[Fe(CN) 6] and 1 mmol/L K4 Fe(CN) 6
) were well mixed and introduced into a 5 mL-beaker. The glassy carbon electrodes were then
immsered in the mixed liquid in the beaker to conduct electrochemical polymerization at room
temperature via cyclic voltammetry under the conditions of a scan rate of 0.05 V/s, a cyclic
voltage of from -0.4 V to +0.7 V, and 15 electropolymerization cycles. After completion of the
polymerization, the electrodes were removed from the beaker and rinsed several times with
deionized water and then dried with nitrogen. The electrodes so modified were referred to as
GCEs/PPy herein. Then, the GCEs/PPy were immersed in a buffer solution (that is a 0.1 mol/L
potassium chloride solution containing 1 mmol/L K3[Fe(CN) 6 ] and 1 mmol/L K4 Fe(CN) 6), and
EIS measurement was then performed thereon.
[78] Comparative Example 3
[79] Surfaces of glassy carbon electrodes were ground and polished with a suspension of
aluminium oxide particles having a particle size of 0.05 to 0.3 m. Thereafter, the electrodes
were ultrasonically cleaned in deionized water and ethanol each for 30 s, and then dried with
nitrogen. 17 L of pyrrole (functional monomer), 0.1 L of CuPcTs (dopant) and 4 mL of a
buffer solution (that is a 0.1 mol/L potassium chloride solution containing 1 mmol/L
K3[Fe(CN) 6] and 1 mmol/L K 4 Fe(CN) 6) were well mixed and introduced into a 5 mL-beaker.
The glassy carbon electrodes were then immersed in the mixed liquid in the beaker to conduct
electrochemical polymerization at room temperature via cyclic voltammetry under the
conditions of a scan rate of 0.05 V/s, a cyclic voltage of from -0.4 V to +0.7 V, and 15
electropolymerization cycles. After completion of the polymerization, the electrodes were
removed from the beaker and were rinsed several times with deionized water and then dried
with nitrogen. The electrodes so modified were referred to as GCEs/PPy-CuPcTs herein. Then,
the GCEs/PPy-CuPcTs were immersed in a buffer solution (that is a 0.1 mol/L potassium
chloride solution containing 1 mmol/L K3[Fe(CN) 6] and 1 mmol/L K 4 Fe(CN) 6), and EIS
measurement was then performed thereon.
[80] FIG. 5 shows EIS data for GCEs/bare, GCEs/PPy, and GCEs/PPy-CuPcTs in the buffer solution. It can be seen from this figure that GCEs/bare, GCEs/PPy, and GCEs/PPy-CuPcTs had an impedance of 150, 200, and 40 Q, respectively. Thus, the impedance of GCEs/PPy-CuPcTs was 3.75 times lower than GCEs/bare, and was 5 times lower than GCEs/PPy.

Claims (5)

1. A method for preparation of a molecularly imprinted polymer for detecting bacteria,
comprising steps of:
(a) adding bacteria serving as a template molecular that is used for imprinting, a
functional monomer, and a dopant to a buffer solution at a predetermined ratio to form a mixed
liquid, into which electrodes are immersed to conduct an electrochemical polymerization
reaction so as to form a conducting polymer on surfaces of the electrodes; and
(b) placing the electrodes having the conducting polymer formed thereon in an elution
solution to remove the template bacteria, followed by drying of the electrodes with a protective
gas, so as to obtain a molecularly imprinted polymer for detecting the bacteria on the surfaces
of the electrodes;
wherein the template bacteria is Listeria monocytogenes, Staphylococcus aureus,
Salmonella, or Escherichia coli 0157:H7 species;
the dopant is copper tetrasulfonatophthalocyanine; and
the functional monomer is pyrrole.
2. The method according to claim 1, wherein the predetermined ratio of the template
bacteria, the functional monomer, and the dopant is 500:17:(0.05-0.25) by volume.
3. The method according to claim 1, wherein the electrochemical polymerization reaction
in the step (a) is conducted via cyclic voltammetry, that is, when the electrodes are immersed in
the mixed liquid, scan parameters and the number of electropolymerization cycles are set to
predetermined values so as to carry out the electrochemical polymerization reaction.
4. The method according to claim 3, wherein the scan parameters include a scan rate and a
cyclic voltage, which are set to 0.05 V/s and -0.4 to +0.7 V, respectively; and wherein, the
number of electropolymerization cycles is set to 5 to 20.
5. A molecularly imprinted polymer prepared according to the method any one of claims 1
to 4.
AU2021104855A 2021-08-03 2021-08-03 Molecularly imprinted polymer for detecting bacteria, and its preparation and use in bacterial detection Ceased AU2021104855A4 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
AU2021104855A AU2021104855A4 (en) 2021-08-03 2021-08-03 Molecularly imprinted polymer for detecting bacteria, and its preparation and use in bacterial detection

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
AU2021104855A AU2021104855A4 (en) 2021-08-03 2021-08-03 Molecularly imprinted polymer for detecting bacteria, and its preparation and use in bacterial detection

Publications (1)

Publication Number Publication Date
AU2021104855A4 true AU2021104855A4 (en) 2021-09-30

Family

ID=77857817

Family Applications (1)

Application Number Title Priority Date Filing Date
AU2021104855A Ceased AU2021104855A4 (en) 2021-08-03 2021-08-03 Molecularly imprinted polymer for detecting bacteria, and its preparation and use in bacterial detection

Country Status (1)

Country Link
AU (1) AU2021104855A4 (en)

Similar Documents

Publication Publication Date Title
Kannan et al. A review on chemical and electrochemical methodologies for the sensing of biogenic amines
Wang et al. Methods for the detection and determination of nitrite and nitrate: A review
Wang et al. Efficient separation and quantitative detection of Listeria monocytogenes based on screen-printed interdigitated electrode, urease and magnetic nanoparticles
Meshram et al. Biosensor and its application in food and dairy industry: a review
Thakur et al. Polyaniline nanoparticle based colorimetric sensor for monitoring bacterial growth
Wang et al. An electrochemical aptasensor using coaxial capillary with magnetic nanoparticle, urease catalysis and PCB electrode for rapid and sensitive detection of Escherichia coli O157: H7
Fernández-Baldo et al. Determination of Ochratoxin A in apples contaminated with Aspergillus ochraceus by using a microfluidic competitive immunosensor with magnetic nanoparticles
CN112280831A (en) Preparation method and application of electrochemical biosensor based on DNA walker
Gürkan et al. Determination of total Sn in some canned beverages by FAAS after separation and preconcentration
CN109490264A (en) Based on the homogeneous label-free detection method of the luminous both-end complementary nucleic acid aptamers probe of aggregation and aflatoxin B1
Fung et al. Analysis of organic acids and inorganic anions in beverage drinks by capillary electrophoresis
Mortari et al. An unconventional approach to impedance microbiology: detection of culture media conductivity variations due to bacteriophage generated lyses of host bacteria
CN114460054B (en) Quantum dot-MXene fluorescent sensor and preparation method and application thereof
AU2021104855A4 (en) Molecularly imprinted polymer for detecting bacteria, and its preparation and use in bacterial detection
Azenha et al. The influence of Cu concentration on ethanolic fermentation by Saccharomyces cerevisiae
Dou et al. An indirect competitive fluorescence assay for ochratoxin A based on molecular beacon
Nagles et al. Determination of Allura Red in the presence of cetylpyridinium bromide by square-wave adsorptive stripping voltammetry on a glassy carbon electrode
CN112980434A (en) Silicon quantum dot for detecting chlorogenic acid and chlorogenic acid detection method
CN109307667B (en) Rapid detection method of aflatoxin B1
CN111693586A (en) Bacterial molecularly imprinted polymer, preparation method thereof and bacterial detection method
Wu et al. A DNAzyme-based electrochemical impedance biosensor for highly sensitive detection of Cu2+ ions in aqueous solution
Tang et al. Hairpin DNA‐Dependent Click Conjugation of Oligonucleotides for Electrochemical Monitoring of Copper (II)
CN112485318A (en) Electrochemical method and device for detecting bisphenol A by nano platinum modified electrode
Chen et al. Carbazole as fluorescence carrier for preparation of doxycycline sensor
Wang et al. Copper ion-selective fluorescent sensor using salicyl fluorone immobilized on a glutaraldehyde-coated eggshell membrane

Legal Events

Date Code Title Description
FGI Letters patent sealed or granted (innovation patent)
MK22 Patent ceased section 143a(d), or expired - non payment of renewal fee or expiry