CN109060902A - The functional nucleic acid modified electrode that lead ion detection method is integrated with probe in lake water water sample - Google Patents
The functional nucleic acid modified electrode that lead ion detection method is integrated with probe in lake water water sample Download PDFInfo
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- CN109060902A CN109060902A CN201811258669.5A CN201811258669A CN109060902A CN 109060902 A CN109060902 A CN 109060902A CN 201811258669 A CN201811258669 A CN 201811258669A CN 109060902 A CN109060902 A CN 109060902A
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- G01N27/28—Electrolytic cell components
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- G01N27/327—Biochemical electrodes, e.g. electrical or mechanical details for in vitro measurements
- G01N27/3275—Sensing specific biomolecules, e.g. nucleic acid strands, based on an electrode surface reaction
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- G01N27/48—Systems using polarography, i.e. measuring changes in current under a slowly-varying voltage
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Abstract
The invention discloses the functional nucleic acid modified electrodes that lead ion detection method in a kind of lake water water sample is integrated with probe, the detection method is that the functional nucleic acid modified electrode for integrating probe immerses buffer 20 ~ 30 minutes added with lead ion to be measured, takes out washing and in the NaClO of 0.1M4DPV measurement is carried out in electrolyte solution, and the plumbum ion concentration in sample is calculated according to the change rate for the DPV peak current signal for scanning record within the scope of 0.1~0.6V.The present invention is selectively good, sensitive, easy, quick.
Description
The application is application number: 201610372050.1, the applying date: 2016-05-31, title " the integrated function core of probe
The divisional application of sour modified electrode Direct Electrochemistry detection lead ion method ".
Technical field
The present invention relates to the functional nucleic acid modified electrode Direct Electrochemistries that a kind of probe integrates to detect lead ion method.
Background technique
Lead ion is a kind of common harmful heavy metal ions, and monitoring/detection has human health and environmental monitoring
Highly important meaning.In the past few decades, people are had been developed such as Atomic absorption/emission spectrum, fluorescence spectrum, matter
A variety of methods such as spectrum, photonic crystal are monitored/detect to lead ion.In recent years, Lu Yi research group in the U.S. by sieving in vitro
Selecting technology obtains the functional nucleic acid 17E DNAzyme sensitive to lead ion, they are identified using 17E DNAzyme as lead ion
Element uses gold nanoparticle as sensing element, develops colorimetric sensor detection lead ion (Liu, J.; Lu, Y.,
Nature Protocols 2006, 1, 246-252.).Wang group is based on 17E DNAzyme and and double-stranded DNA fluorescence
Molecule chelating dyes Picogreen has developed label-free fluorescent optical sensor detection lead ion (Zhang, L.; Han, B.;
Li, T.; Wang, E., Chemical Communications 2011, 47, 3099–3101.).Then, Yin group
Electrochemical luminescence sensor detection lead ion (Gao, A. are developed based on 17E DNAzyme; Tang, C.; He, X.;
Yin, X., Analyst, 2013, 138, 263–268).Therefore the functional nucleic acid 17E DNAzyme of lead ion sensitivity is utilized
Detection lead ion receives the extensive concern of domestic and international expert.
Since the detection of fluorescence detection, ultraviolet detection and electrochemical luminescence requires huger, valuable detecting instrument,
Therefore these methods are not suitable for the occasion of some simpler and cruder yards field work in one's power.Electrochemical detection method due to
Have many advantages, such as high sensitivity, it is easy to operate it is quick, at low cost, low energy consumption, is easy to instrumentation, thus day by researcher
Benefit favor.
Summary of the invention
The purpose of the present invention is to provide a kind of selectivity, and the integrated functional nucleic acid of good, sensitive, easy, quick probe is repaired
It adorns electrode Direct Electrochemistry and detects lead ion method.
The technical solution of the invention is as follows:
A kind of functional nucleic acid modified electrode Direct Electrochemistry detection lead ion method that probe is integrated, it is characterized in that: by probe collection
At functional nucleic acid modified electrode immerse added with buffer 20 ~ 30 minutes of lead ion to be measured, take out washing and 0.1 M's
NaClO4DPV measurement is carried out in electrolyte solution, according to the DPV peak current signal for scanning record within the scope of 0.1~0.6V
Change rate calculates the plumbum ion concentration in sample;The buffer is pH 7.5,20 containing 140 mM NaCl and 5 mM KCl
MM Tris-HCl solution;
The integrated functional nucleic acid modified electrode of the probe is prepared by following methods: gold nanoparticle modified electrode is placed in
Self assembly 10 ~ 18 hours in buffer solution added with 1 μM of mercapto-modified 17E DNAzyme;The buffer be pH 7.5,
The 20 mM Tris-HCl solution containing 140 mM NaCl and 5 mM KCl;It takes out electrode to be cleaned with the buffer solution, then will be electric
Pole is placed in the above-mentioned buffer solution added with 1mM sulfydryls hexanol and is passivated 1-3 hours, cleans removing not with same buffer solution
The mercaptoethanol of assembling;Finally electrode is transferred in the substrate 17DS solution containing 1 μM and is assembled 10 ~ 18 hours;The substrate
The terminal modified ferrocene probe molecule in the 3 ' of 17DS;Electrode is washed 2-3 times with above-mentioned buffer solution again, obtains the integrated function of probe
Nucleic acid modified electrode.
The integrated functional nucleic acid modified electrode of probe immerses buffer 25 minutes added with lead ion to be measured.
Gold nanoparticle modified electrode is placed in the buffer solution added with 1 μM of mercapto-modified 17E DNAzyme from group
It fills 12 hours.
Finally electrode is transferred in the substrate 17DS solution containing 1 μM and is assembled 12 hours.
The invention has the benefit that
1. the identification molecule that the present invention is detected using functional nucleic acid 17E DNAzyme as lead ion, selectivity is good, to environment
It is without secondary pollution.
2. detected using electrochemical method, have high sensitivity, instrument it is simple, it is easy to operate quickly, low cost and low energy
The advantages that consumption.
3. this method is integrated into electrode surface, is not necessarily in detection process using the method for probe and substrate chain 17DS integration
Additional electrochemical probe reagent is added in electrolyte solution, the degree of integration of electrode is high, functional, and detection convenience mentions
It is high.
Detailed description of the invention
Present invention will be further explained below with reference to the attached drawings and examples.
Fig. 1 is the DPV curvilinear motion figure in the present invention to the modified electrode measured during lead at different concentrations ion detection.
Fig. 2 is the standard working curve figure that modified electrode of the invention detects lead ion.
Specific embodiment
(1) preparation of the integrated functional nucleic acid modified electrode of probe
Gold nanoparticle modified electrode is placed in self assembly 12 in the buffer solution added with 1 μM of mercapto-modified 17E DNAzyme
Hour;The buffer is pH 7.5, the 20 mM Tris-HCl solution containing 140 mM NaCl and 5 mM KCl;Take out electrode
It is cleaned with the buffer solution, then electrode is placed in the above-mentioned buffer solution added with 1mM sulfydryls hexanol and is passivated 2 hours, used
Same buffer solution cleaning removes unassembled mercaptoethanol;Electrode is finally transferred to the substrate 17DS solution containing 1 μM
Middle assembling 12 hours;The terminal modified ferrocene probe molecule in the 3 ' of the substrate 17DS;Electrode 3 is washed with above-mentioned buffer solution again
It is secondary, obtain the integrated functional nucleic acid modified electrode of probe.
(2) in lake water water sample lead ion detection
The modified electrode prepared is immersed in a series of buffer solutions added with the lead ion standard water sample of various concentration and is soaked
After steeping 25 min, with above-mentioned buffer solution cleaning electrode 2 times;With the NaClO of 0.1 M4As supporting electrolyte solution, carry out
DPV sweep test, test parameter are as follows: adjustment time is 50 ms, and interval time is 0.5 s, and modulated amplitude is 50 mV, step electricity
Gesture is 5 mV, and scanning range is 0.1~0.6V.Using DPV peak current as ordinate, plumbum ion concentration is abscissa, draws standard
Working curve, as shown in Figure 2.
Using lake water as actual sample, lake water after active carbon decoloring with 0.22 μm of membrane filtration, then with 15000
Turn/min centrifugation after, take supernatant to be measured.The 50 μ L lake water water sample handled well is added in above-mentioned buffer solution, is pressed
According to said determination step operation, its DPV peak current is measured, according to DPV peak current change rate (I0-I)/I0, intended by standard curve
It is 327 pM that the linear equation of conjunction, which can calculate plumbum ion concentration in water sample,.
Claims (1)
1. the functional nucleic acid modified electrode that lead ion detection method is integrated with probe in a kind of lake water water sample, it is characterized in that: described
Lead ion detection method is in lake water water sample: the modified electrode prepared is immersed in a series of lead ions added with various concentration
After impregnating 25 min in the buffer solution of standard water sample, with above-mentioned buffer solution cleaning electrode;With the NaClO of 0.1 M4As branch
Electrolyte solution is held, DPV sweep test, test parameter are carried out are as follows: adjustment time is 50 ms, and interval time is 0.5 s, modulation
Amplitude is 50 mV, and step potential is 5 mV, and scanning range is 0.1~0.6V;Using DPV peak current as ordinate, plumbum ion concentration
For abscissa, standard working curve is drawn;
Using lake water as sample, lake water after active carbon decoloring with 0.22 μm of membrane filtration, then with 15000 turns/min from
After the heart, supernatant is taken to be measured;The 50 μ L lake water water sample handled well is added in above-mentioned buffer solution, according to above-mentioned survey
Determine step operation, measure its DPV peak current, according to DPV peak current change rate (I0-I)/I0, by the linear of standard curve fit
Equation can calculate plumbum ion concentration in water sample;
The modified electrode is the functional nucleic acid modified electrode that probe integrates, and is prepared by following method: by gold nanoparticle
Modified electrode is placed in self assembly about 12 hours in the buffer solution added with 1 μM of mercapto-modified 17E DNAzyme;The buffering
Solution is pH 7.5, the 20 mM Tris-HCl solution containing 140 mM NaCl and 5 mM KCl;It is molten with the buffering to take out electrode
Liquid cleaning, then electrode is placed in the above-mentioned buffer solution added with 1mM sulfydryls hexanol and is passivated, it is cleaned with same buffer solution
Remove unassembled mercaptoethanol;Finally electrode is transferred in the substrate 17DS solution containing 1 μM and is assembled;The substrate
The terminal modified ferrocene probe molecule in the 3 ' of 17DS;Electrode is washed with above-mentioned buffer solution again, obtains the integrated functional nucleic acid of probe
Modified electrode.
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CN201811258669.5A CN109060902A (en) | 2016-05-31 | 2016-05-31 | The functional nucleic acid modified electrode that lead ion detection method is integrated with probe in lake water water sample |
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CN201610372050.1A CN105891286B (en) | 2016-05-31 | 2016-05-31 | The integrated functional nucleic acid modified electrode Direct Electrochemistry of probe detects lead ion method |
CN201811258669.5A CN109060902A (en) | 2016-05-31 | 2016-05-31 | The functional nucleic acid modified electrode that lead ion detection method is integrated with probe in lake water water sample |
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CN201811258669.5A Pending CN109060902A (en) | 2016-05-31 | 2016-05-31 | The functional nucleic acid modified electrode that lead ion detection method is integrated with probe in lake water water sample |
CN201610372050.1A Expired - Fee Related CN105891286B (en) | 2016-05-31 | 2016-05-31 | The integrated functional nucleic acid modified electrode Direct Electrochemistry of probe detects lead ion method |
CN201811258719.XA Pending CN109187695A (en) | 2016-05-31 | 2016-05-31 | Application of the probe integrated functionality nucleic acid modified electrode in lake water water sample in lead ion detection |
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CN201811258719.XA Pending CN109187695A (en) | 2016-05-31 | 2016-05-31 | Application of the probe integrated functionality nucleic acid modified electrode in lake water water sample in lead ion detection |
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CN106442345B (en) * | 2016-09-08 | 2019-03-15 | 常熟理工学院 | A kind of lead ion detection method based on CD spectrum detection technique |
CN107843637A (en) * | 2017-10-12 | 2018-03-27 | 辽宁师范大学 | For detecting the block polymer decorated electrode and preparation method of lead ion |
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CN101363795A (en) * | 2008-08-11 | 2009-02-11 | 中国科学院长春应用化学研究所 | Unmarked colorimetric determination metallic lead ion method based on aurum nanometer probe and nuclease |
CN102375020A (en) * | 2010-08-19 | 2012-03-14 | 华东师范大学 | Method for detecting mercury ions through gold electrode modified by polythymidine DNA |
CN102031284B (en) * | 2010-11-04 | 2015-07-29 | 中国科学院上海微系统与信息技术研究所 | A kind of lead ion detection chip based on picodna enzyme, making and using method |
CN103123333B (en) * | 2012-12-31 | 2016-03-02 | 北京师范大学 | Based on the method for three electrode sensors and Differential Pulse Voltammetry Fast Measurement lead |
CN104569085B (en) * | 2013-10-28 | 2019-04-02 | 南京大学 | The mercury metal ion electrochemical sensor of highly sensitive high selection |
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CN104020204B (en) * | 2014-06-19 | 2016-08-24 | 湖南大学 | A kind of for electrochemical sensor detecting lead and its preparation method and application |
CN104914151B (en) * | 2015-05-08 | 2017-10-13 | 首都师范大学 | It is a kind of to be used for the forming method and its electrochemical sensor of ampicillin and sulfadimethoxine electrochemical sensor self assembly passivation layer |
CN105223250B (en) * | 2015-09-23 | 2018-01-02 | 南京邮电大学 | Double stem ring DNA electrochemical sensors of polyA overseas Chinese federations and its preparation and application |
CN105445350A (en) * | 2015-11-13 | 2016-03-30 | 南京理工大学 | Electrochemical DNA (Deoxyribose Nucleic Acid) biosensor based on peptide nucleic acid and preparation method of electrochemical DNA biosensor |
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CN105891286B (en) | 2018-12-18 |
CN109187695A (en) | 2019-01-11 |
CN109060903A (en) | 2018-12-21 |
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Application publication date: 20181221 |